The effect of cosolvent on trace free water in the determination of the contamination degree of jet fuel was investigated. The interference of trace free water on the automatic particle counter can be eliminated by adding isopropanol as a cosolvent to the measured oil sample. Isopropanol can dissolve trace free water in oil. Addition of isopropanol could stabilize the pollution grade of particles with size ≥30 μm (c) at the same level, which is most obviously affected by free water without isopropanol. The standard uncertainty u(X 1) is slightly reduced with the addition of isopropanol, and the repeatability and accuracy of the automatic particle counting method are obviously improved. The results show that isopropanol should be added as a cosolvent to eliminate the interference of free water when the contamination degree of jet fuel oil samples with obvious free water is determined by the automatic particle counting method.
The effect of cosolvent on trace free water in the determination of the contamination degree of jet fuel was investigated. The interference of trace free water on the automatic particle counter can be eliminated by adding isopropanol as a cosolvent to the measured oil sample. Isopropanol can dissolve trace free water in oil. Addition of isopropanol could stabilize the pollution grade of particles with size ≥30 μm (c) at the same level, which is most obviously affected by free water without isopropanol. The standard uncertainty u(X 1) is slightly reduced with the addition of isopropanol, and the repeatability and accuracy of the automatic particle counting method are obviously improved. The results show that isopropanol should be added as a cosolvent to eliminate the interference of free water when the contamination degree of jet fuel oil samples with obvious free water is determined by the automatic particle counting method.
The automatic particle counter is an instrument
that uses optical
sensors to measure solid particles in oil, which can directly detect
oil in the laboratory or on-line. It can measure the distribution
of particle number and size.[1−3] According to the equivalent projection
particle size, the light flux, which is blocked by particles, is received
through the shading sensor and converted into electrical signals,
which are transmitted to the counter through the preamplifier for
counting. However, the trace free water suspended in jet fuel can
also shield the light, which interferes with the results of the automatic
particle counting method.[4−7]Domestic research lacks the application of
automatic particle counter
in the field of jet fuel.[8−10] In contrast, foreign research
on the application of particle counter in the field of jet fuel is
more, mainly exploring the feasibility of using this method, but few
standards have been formed. In recent years, British Energy Institute
has proposed a test standard for detecting fuel particulate pollutants
by sensors.[11−13] There are three standards: IP 564 (Cleanliness Measurement
of Aviation Turbine Fuel—Laboratory Automatic Particle Counter
Method), IP 565 (Cleanliness Measurement of Aviation Turbine Fuel—Portable
Automatic Particle Counter Method), and IP 577 (Cleanliness Measurement
of Aviation Turbine Fuel—Shaded Automatic Particle Counter
Method).Because the application time of the particle counter
method in
the jet fuel field is still short, there is no mature and effective
standard method for monitoring jet fuel quality using sensors in the
United States. Only TARDEC of the U.S. Army put forward a monitoring
method proposal,[12] which uses the 19/17/14/13
grade of 4 μm (c)/6 μm (c)/14 μm (c)/30 μm
(c) particle size in ISO 4406 pollution level standard for the quality
control requirement of jet fuel contamination. The USA TARDEC has
systematically studied the feasibility of applying a particle counter
in the jet fuel field and evaluated the application prospects of particle
counter from many aspects, especially eliminating the influence of
free water on the results of particle counter.[12] Therefore, isopropanol was selected as the cosolvent to
evaluate the effect of cosolvent on the determination results.
Results
and Discussion
Effect of Container Materials on the Determination
of the Contamination
Degree of Jet Fuel
As Table shows, the contamination degrees of oil samples have
not changed significantly, and the repeatability of the test is good.
The influence of free water on the automatic particle counter is basically
eliminated by using a glass bottle. The chemical composition of the
glass bottle is mainly silica, which may absorb part of water from
oil samples by a hydrogen bond. When free water is adsorbed on the
wall of the glass bottle, the result of particle counting of oil samples
would naturally decrease. Although the glass bottle eliminated the
influence of free water, it had a negative impact on the determination
of contamination degrees, and the automatic particle counter could
not truly reflect the situation of free water in oil samples, which
is not conducive to the comprehensive evaluation of the quality of
fuel.
Table 1
Determination of Particle Quantity
and Grade of Samples in a Glass Bottle
ACM
20
sample
particle (mg/L)
free water (ppm)
≥4 μm (c)
≥6 μm (c)
≥14 μm (c)
≥30 μm (c)
1
1.0
0
2410.4/18
913.6/17
49.8/13
1.0/7
2
1.0
5
2150.4/18
953.3/17
58.9/13
2.0/8
3
1.0
10
2616.6/19
1116.1/17
66.7/13
2.7/9
4
1.0
20
2363.9/18
1026.5/17
65.4/13
3.6/9
5
1.0
30
2848.6/19
1200.9/17
59.4/13
2.6/9
6
2.0
0
4341.4/19
1446.6/18
62.1/13
3.6/9
7
2.0
5
4982.1/19
1795.7/18
76.5/13
4.1/9
8
2.0
10
5108.1/20
1685.6/18
60.4/13
2.0/8
9
2.0
20
5333.9/20
1906.4/18
85.8/14
3.9/9
10
2.0
30
4395.2/19
1431.9/18
57.3/13
2.5/8
11
3.0
0
8109.1/20
3206.1/19
141.6/14
8.7/10
12
3.0
5
8536.6/20
3554.9/19
440.4/16
13.1/11
13
3.0
10
7805.3/20
3115.7/19
183.9/15
4.7/9
14
3.0
20
6903.4/20
2618.9/19
154.0/14
8.0/10
15
3.0
30
5716.6/20
2018.0/18
114.4/14
8.6/10
As shown in Table , although the contamination
degrees of oil samples have a certain
linear relationship, there are also some fluctuations. For example,
compared with the no. 2 oil sample, the number of particles in the
no. 4 oil sample decreases. There is a linear relationship between
the number of particles with different particle sizes [≥4 μm
(c) and ≥6 μm (c)]. However, the results of contamination
degrees fluctuate when there are particles with large sizes [≥14
μm (c) and ≥30 μm (c)] in oil samples, especially,
oil samples with particle size ≥30 μm (c). The main reason
may be that the larger the particle size, the more likely it is to
be unevenly distributed in the oils. The results of contamination
degrees of oil samples are basically kept at the same pollution level,
except oil samples with particle size ≥30 μm (c).
Table 2
Determination of Particle Quantity
and Grade of Samples in a Metal Bottle
ACM
20
sample
particle (mg/L)
free water (ppm)
≥4 μm (c)
≥6 μm (c)
≥14 μm (c)
≥30 μm (c)
1
1.0
0
3940.3/19
1751.4/18
126.6/14
4.1/9
2
1.0
5
3761.7/19
1571.3/18
105.0/14
4.9/9
3
1.0
10
4187.1/19
1756.4/18
108.7/14
3.7/9
4
1.0
20
5455.6/19
1855.8/18
71.4/13
4.7/9
5
1.0
30
5768.9/19
1915.1/18
109.0/14
4.4/9
6
2.0
0
3895.9/19
1586.9/18
141.6/14
21.6/12
7
2.0
5
4768.7/19
1986.9/18
126.1/14
6.9/10
8
2.0
10
6788.6/20
2581.4/19
141.4/14
3.4/9
9
2.0
20
7573.9/20
2989.0/19
168.4/15
8.0/10
10
2.0
30
8492.8/19
2758.0/18
171.8/14
6.0/10
11
3.0
0
6180.0/20
2460.2/18
138.9/14
15.1/11
12
3.0
5
7499.0/20
3197.1/19
183.6/15
6.4/10
13
3.0
10
7852.6/20
3264.4/19
166.7/15
12.6/11
14
3.0
20
8389.5/20
4000.0/19
180.4/15
7.4/10
15
3.0
30
10,152.9/21
4420.4/19
329.2/16
18.9/11
As Table exhibits,
the number of particles shows a certain linear relationship, especially,
the number of particles with particle sizes ≥4 μm (c)
and ≥6 μm (c). Theoretically, when the number of small
size particles is more, their distribution is more uniform. Compared
with the results of plastic bottles and metal bottles, it seems that
the results of plastic bottles were better. Similar to the results
of metal bottles, the contamination degrees of oil samples are at
the same level within the repeatability range.
Table 3
Determination of Particle Quantity
and Grade of Samples in a Plastic Bottle without Isopropanol
ACM
20
sample
particle (mg/L)
free water (ppm)
≥4 μm (c)
≥6 μm (c)
≥14 μm (c)
≥30 μm (c)
1
1.0
0
2513.1/19
1141.7/17
74.2/13
1.1/7
2
1.0
5
2006.8/18
947.3/17
65.7/13
1.4/8
3
1.0
10
3020.6/19
1366.2/18
107.0/14
1.6/8
4
1.0
20
2712.3/19
1205.1/17
75.9/13
0.9/7
5
1.0
30
3371.8/19
1548.1/18
107.4/14
2.6/9
6
2.0
0
3884.4/19
1355.0/18
77.7/13
3.4/9
7
2.0
5
3639.3/19
1261.4/17
73.1/13
9.6/10
8
2.0
10
4434.9/19
1499.1/18
60.1/13
3.6/9
9
2.0
20
4442.2/19
1474.6/18
58.9/13
2.2/8
10
2.0
30
5189.0/20
1789.4/18
110.8/14
12.4/11
11
3.0
0
3120.2/19
1146.7/17
90.7/14
7.4/10
12
3.0
5
5322.4/20
1909.1/18
73.4/13
3.4/9
13
3.0
10
5979.3/20
2244.1/18
110.0/14
7.9/10
14
3.0
20
6216.4/20
2308.1/18
117.3/14
7.3/10
15
3.0
30
7301.9/20
2844.4/19
155.2/14
5.4/10
Above all, plastic material is more suitable
for the material of
oil container and would be used to investigate the effect of cosolvent
in eliminating the interference of free water on the determination
of the contamination degree of jet fuel.
Effect of Additives on
the Elimination of Free Water for Particle
Counting
The contamination degrees of oil samples without
or with cosolvents are determined sequentially and listed in Tables and 4 respectively. According to the U.S. Army’s recommendations
for the detection of the contamination degree of jet fuel, the contamination
degrees of particles with different sizes [≥4 μm (c),
≥6 μm (c), ≥14 μm (c), and ≥30 μm
(c)] are detected, which were determined according to ISO 4406 standard
for its corresponding number and grade.
Table 4
Determination
of Particle Quantity
and Grade of Samples in a Plastic Bottle with Isopropanol
ACM
20
sample
particle (mg/L)
free water (ppm)
≥4 μm (c)
≥6 μm (c)
≥14 μm (c)
≥30 μm (c)
1
1.0
0
3288.9/19
1460.3/18
149.1/14
8.5/10
2
1.0
5
3423.6/19
1375.9/18
92.7/14
3.0/9
3
1.0
10
3353.6/19
1387.1/18
82.1/14
2.1/8
4
1.0
20
3446.4/19
1408.6/18
92.7/14
2.6/9
5
1.0
30
3534.9/19
1462.2/18
92.1/14
2.9/9
6
2.0
0
3486.7/19
1523.0/18
91.1/14
2.8/9
7
2.0
5
4021.4/19
1816.6/18
146.1/14
4.6/9
8
2.0
10
3792.2/19
1648.9/18
137.1/14
4.9/9
9
2.0
20
3766.7/19
1576.4/18
107.2/14
2.9/9
10
2.0
30
3697.1/19
1630.4/18
159.3/14
4.7/9
11
3.0
0
7753.1/20
3355.9/19
190.7/15
5.0/9
12
3.0
5
7721.1/20
3214.9/19
152.1/14
2.0/8
13
3.0
10
7543.9/20
3235.1/19
164.4/15
3.6/9
14
3.0
20
7590.4/20
3225.6/19
155.7/14
3.1/9
15
3.0
30
7691.3/20
3258.9/19
180.4/15
3.6/9
As Figures –4 show, the
number of particles [≥4 μm (c), ≥6 μm (c),
≥14 μm (c), and ≥30 μm (c)] shows a certain
linear relationship with free water, and especially, the number of
particles ≥4 μm (c) and ≥6 μm (c) has a
better linear relationship. Theoretically, more small size particles
could result in their more uniform distribution. The linear relationship
shows that the existence of free water can improve the counting results
of the automatic particle counter, which has an interference effect
on the determination of jet fuel contamination. Moreover, the analysis
results show that except for particles with particle size ≥30
μm (c), the pollution levels of other particles are at the same
level, and the results are within the repeatability range, indicating
that the error effect of free water can be partially eliminated when
the pollution level is divided.
Figure 1
Determination results of ≥4 μm
(c) granules before
addition of isopropanol.
Figure 4
Determination results
of ≥30 μm (c) granules before
addition of isopropanol.
Determination results of ≥4 μm
(c) granules before
addition of isopropanol.Determination results
of ≥6 μm (c) granules before
addition of isopropanol.Determination results
of ≥14 μm (c) granules before
addition of isopropanol.Determination results
of ≥30 μm (c) granules before
addition of isopropanol.As exhibited in Figures and 6, the counting results of particles
with sizes 4 μm (c) and 6 μm (c) tend to be stable. The
stability of the measured results of particles ≥4 μm
(c) and (≥6 μm (c) is obviously better than those particles
≥14 μm (c) and ≥30 μm (c). In theory, according
to the statistical analysis, less number of large size particles could
cause uneven distribution. Even so, comparing Figures and 8 with Figures and 4, the results of determination tend to be more stable after
adding isopropanol, and the impact of impurities in free water is
basically eliminated.
Figure 5
Determination results of ≥4 μm (c) granules
after
addition of isopropanol.
Figure 6
Determination results
of ≥6 μm (c) granules after
addition of isopropanol.
Figure 7
Determination results
of ≥14 μm (c) granules after
addition of isopropanol.
Figure 8
Determination results
of ≥30 μm (c) granules after
addition of isopropanol.
Figure 3
Determination results
of ≥14 μm (c) granules before
addition of isopropanol.
Determination results of ≥4 μm (c) granules
after
addition of isopropanol.Determination results
of ≥6 μm (c) granules after
addition of isopropanol.Determination results
of ≥14 μm (c) granules after
addition of isopropanol.Determination results
of ≥30 μm (c) granules after
addition of isopropanol.As Figures and 10 show, the
number of large-sized particles [mainly
>30 μm (c)] in samples without isopropanol increases along
with
the increase of water content, indicating that the existence of free
water will lead to changes in the counting results. In contrast, after
adding isopropanol, the volume fraction of particles [>30 μm
(c)] decreases significantly and drops to less than 10%. Moreover,
the difference between the determination results of different moisture
contents is significantly reduced, which shows that isopropanol as
a cosolvent can effectively eliminate the interference effect of free
water and significantly improve the repeatability of the determination
method.
Figure 9
Particle volume percent of different particle sizes before addition
of isopropanol.
Figure 10
Particle volume percent of different
particle sizes after addition
of isopropanol.
Particle volume percent of different particle sizes before addition
of isopropanol.Particle volume percent of different
particle sizes after addition
of isopropanol.In summary, the results
in Table and Figures –8 show that the counting results
are more stable. Particles with sizes greater than 4, 6, and 16 μm
(c) are almost maintained at the same pollution level, which is more
reproducible than those results without cosolvents. Moreover, the
counting level of particles with sizes greater than 30 μm (c)
is stabilized at the same level by adding cosolvents with less than
1 level of deviation. The results show that the addition of cosolvent
basically eliminates the influence of free water on the automatic
particle counter with a remarkable effect. The effect of isopropanol
is attributed to the addition of isopropanol in jet fuel. Isopropanol
contains not only the polar group hydroxyl (−OH) but also the
nonpolar group methyl (−CH3). The polar group in
isopropanol can be dissolved in water, whereas the nonpolar group
isobutyl can be dissolved in jet fuel. As a result, the solubility
of water in jet fuel increases due to the presence of isopropanol,
which leads to the increase of water jet fuel solubility, and the
phase separation zone decreases and the maximum temperature of mutual
solubility decreases. Therefore, isopropanol combined with water can
be dissolved in jet fuel so that the free water in jet fuel is eliminated
and the influence of free water is eliminated, and isopropanol, as
a cosolvent, is better than isobutanol, butanol, and other alcohol
cosolvents.
Uncertainty Analysis
In this paper,
uncertainty analysis
is introduced to evaluate the test data in order to verify the accuracy
and repeatability of the object of inquiry in determining the degree
of jet fuel pollution. Uncertainty can be evaluated according to the
error of test data, which is an index to measure the quality of test
data. Generally, the less uncertain the data, the better its accuracy
and repeatability. Therefore, the test data are analyzed with uncertainty
analysis.Because the repeatability of the experimental results
is mainly evaluated, only the standard uncertainty u(X1) is introduced to evaluate the different
repeatability of the results in the uncertainty analysis process.
The uncertainty of the determination results is calculated, and the
schematic diagram is made as follows.As Figure shows,
the uncertainty of particle counting results of each particle size
decreases slightly with the addition of isopropanol as a cosolvent,
and there is a decrease of about 1%, which shows that the addition
of isopropanol can not only dissolve free water in oil but also improve
the repeatability of the test results. In fact, because the shape
of free water is not fixed, the shape of free water may change when
it is dispersed in oil, resulting in poor repeatability.
Figure 11
Uncertainty
analysis without (a) and with (b) isopropanol.
Uncertainty
analysis without (a) and with (b) isopropanol.
Conclusions
The interference of trace free water on the
automatic particle
counter can be eliminated by adding isopropanol as a cosolvent to
the measured oil sample. Isopropanol can dissolve trace free water
in oil. Addition of isopropanol could stabilize the pollution grade
of particles with size ≥30 μm (c) at the same level,
which is most obviously affected by free water without isopropanol.
The standard uncertainty u(X1) is slightly reduced with the addition of isopropanol, and
the repeatability and accuracy of the automatic particle counting
method are obviously improved.The results show that isopropanol
should be added as a cosolvent
to eliminate the interference of free water when the contamination
degree of jet fuel oil samples with obvious free water is determined
by the automatic particle counting method.
Materials and Methods
Reagents
and Materials
No. 3 jet fuel was purchased
from Shanghai Gaoqiao Refinery. N-heptane was purified
for market analysis. Isopropanol and 2,2-dimethoxypropane (DMP) were
purchased from Shanghai China National Medicines Corporation Ltd and
purified for market analysis. ISOMTD dust with ISO 12103-1 standard
was purchased from Shanghai Rebey Trading Co., Ltd. Distilled water
was laboratory self-made. Three kinds of common container materials
are selected: glass, metal, and plastic. Each material container has
1 L capacity.
Test Instrument
ACM 20 automatic
particle counter,
manufactured by American Parker Company, was specially used to detect
the contamination of jet fuel in accordance with the equivalent projection
particle size, which is a portable instrument for rapid detection
of aviation fuel pollutants and can be connected to pipeline on-line
measurement and measure solid particles in jet fuel after sampling.
Preparation of Jet Fuel Containing Saturated Dissolved Water
Jet fuel containing saturated dissolved water was prepared as follows.[14] A 1000 mL glass jug was carefully filled with
100 mL of distilled water so that the sides of the jug would not been
clung by water droplets above the water level. Whatman filter papers
were inserted in the glass jug, keeping the bottom of the paper in
the water. Then, 800 mL of fuel was slowly poured over the water,
avoiding intermingling of the water and fuel. The top of the filter
paper was protruded into the fuel, bringing water up into the fuel.
A closed vent system is provided to allow only water-saturated air
to enter the system to maintain the fuel in a water-saturated condition.
The combination of fuel and water was left in the jug for more than
24 h, and then the water-saturated fuel was removed by a siphon. Then,
the content of saturated dissolved water was determined in accordance
with the method described in our previous study.[15,16] The content of saturated dissolved water was detected with DMP as
the titrant. DMP underwent an endothermic reaction with water under
the catalytic action of acids, and its enthalpy is +27.6 kJ/mol. The
reaction equation is exhibited as eq .
Determination of the Contamination
Degree of Jet Fuel
The initial oil sample was filtered to
ensure that the original particles
were removed, followed by preparation of the oil sample with saturated
dissolved water. Then, three batches of oil samples were prepared
by adding 1, 2, and 3 mg/L of ISOMTD dust. Distilled water of 0,
5, 10, 20, and 30 ppm as free water was added into each batch of oil
sample.Before starting the test, the containers were precleaned
to store the oil samples. The instrument was rinsed three times with
clean n-heptane solution. Then, the cleaned instrument
was carries out with a test operation according to the normal test
operation steps to ensure that the cleanliness of the instrument catheter
is lower enough with the oil sample. Before each test, the contamination
degree of oil samples from 1 to 15 was measured by the automatic particle
counting method with shaking manually for 60 s. The contamination
of no. 1 to no. 15 oil samples was determined repeatedly by adding
isopropanol at a volume fraction of 5.9%. All oil samples were measured
three times with or without isopropanol to obtain the average value.