The analytical information given by different types of instruments was scaled in order to establish suitably the figures of merit of a given methodology based on color measurements. Different lab and portable instruments, including smartphones with and without a miniaturized spectrophotometer accessory, have been tested. In order to obtain broad information and using objective criteria, these instruments have been compared from (1) the analytical point of view, considering mainly the detection limit (limits of detection [LODs]), selectivity, accuracy and intra- and interday precision, size, components, and costs; and (2) the environmental point of view, based on their footprint as kilograms of CO2. No significant differences in the precision were obtained with RSD (%) values lower than 10% for all of the instruments, but the achieved values of LOD, selectivity, accuracy, and cost were different. Footprints of CO2 were better for portable instrumentation, especially for smartphones. Three solid chemosensors made of different materials (PDMS, paper, or nylon) have been tested for the determination of ammonia and hydrogen sulfide at different concentration levels (ppb levels). As a result of this study, some rules for selecting the instrument for obtaining the required information have been established. Two apps have been developed for quantitation by smartphones, one for working with RGB values and the other for spectra obtained by the miniaturized spectrophotometer coupled to a smartphone.
The analytical information given by different types of instruments was scaled in order to establish suitably the figures of merit of a given methodology based on color measurements. Different lab and portable instruments, including smartphones with and without a miniaturized spectrophotometer accessory, have been tested. In order to obtain broad information and using objective criteria, these instruments have been compared from (1) the analytical point of view, considering mainly the detection limit (limits of detection [LODs]), selectivity, accuracy and intra- and interday precision, size, components, and costs; and (2) the environmental point of view, based on their footprint as kilograms of CO2. No significant differences in the precision were obtained with RSD (%) values lower than 10% for all of the instruments, but the achieved values of LOD, selectivity, accuracy, and cost were different. Footprints of CO2 were better for portable instrumentation, especially for smartphones. Three solid chemosensors made of different materials (PDMS, paper, or nylon) have been tested for the determination of ammonia and hydrogen sulfide at different concentration levels (ppb levels). As a result of this study, some rules for selecting the instrument for obtaining the required information have been established. Two apps have been developed for quantitation by smartphones, one for working with RGB values and the other for spectra obtained by the miniaturized spectrophotometer coupled to a smartphone.
Increasing demands
for new devices for monitoring the environment[1,2] and
health,[3] including security and environmental
protection, at the point of the problem have contributed to the development
of portable instrumentation.[4] Portable
spectroscopy is a very significant and growing discipline, and hence,
the number of articles related to this topic in the web of science
(WOS) database has increased considerably in the last 10 years (to
more than 20 000), and 25% of these articles are from the chemistry
field. However, more than 35 000 articles related to smartphones
have been published, of which only 5% are related to chemistry.For solid colorimetric devices, paper,[5] PDMS,[6,7] and cotton[8] were
proposed as supports. Traditionally, color is measured by the naked
eye for qualitative or semiquantitative analysis[9] or by a noninvasive technique such as lab-visible reflectance
spectroscopy (from 380 to 780 nm)[9] for
quantitative analysis. However, there is a possibility of configuring
cheaper portable instruments using portable components and optical
fibers, including a reflection probe.[10,11] Nowadays,
smartphones are widely used by people; thus, they have become a valuable
tool within the framework of in situ analysis. Guo implemented blood
β-ketone monitoring by the utilization of a smartphone-powered
medical dongle as a miniaturized electrochemical analyzer,[12] while Fu et al. presented a palm-sized uric
acid test powered by a smartphone using a photochemical dongle for
proactive gout management.[13] In addition,
Mu et al. reported a nano-SERS chip combined with a smartphone-based
Raman detector for the identification of pesticide residues.[14] Accordingly, in the last decade, new “color
instruments” became available for much lower prices as well,
thanks to digital cameras and smartphones.[15,16] A smartphone can capture images, which can be processed in order
to obtain parameters related to color, such as RGB (red/green/blue)
coordinates[14] or CIElab,[15] among others. Several works have been reported in past
years in analytical chemistry, in which these color coordinates have
been used as analytical signals for calibration.[15−19] This smartphone-based colorimetric test needs illumination
and image processing. However, the image quality can suffer from nonuniform
and nonreproducible lighting, which negatively affects the accuracy
of the measurement. To obtain good measurements, some strategies such
as the use of boxes with light (LEDs)[20] or using the light source of the phone[18] have been proposed to eliminate the interference from ambient light.
But the spectrum provides more selective information of a given analyte.
In this sense, combining the integration of CMOS (complementary metal–oxide–semiconductor)
camera image sensors with an optical grating and a spectrum processing
technique, a portable spectrophotometer can be obtained. Some examples
have been described in the literature based on the smartphone spectrophotometer
design using transmission and reflective diffraction gratings.[21−23] All of the spectrometer components can be integrated into a small
block and can be attached to the phone camera. Because of the small
size and easy portability, this instrument is an alternative to conventional
optical spectroscopic techniques and is suitable for different applications.[24] In terms of software, the data acquisition and
processing capacity of the phone itself play an important role.[25,26]The analytical properties of different measuring instruments
have
been obtained and scaled in this paper for solid chemosensors of ammonia
and hydrogen sulfide as use cases (see Table S1 for the type of samples and levels of concentration).[27−29] The smartphone (coupled or not to a miniaturized spectrometer) and
portable reflectance instruments have been compared with a laboratory
reflectance instrument. First, a protocol guide to perform suitable
measurements using a smartphone has been established employing a set
of 45 colors, and two apps were developed for quantitation by the
smartphones: one for RGB values and the other for spectra obtained
by the miniaturized spectrophotometer coupled to a smartphone; several
smartphones were also tested. Then, a comparative study for all instruments,
analytical and environmental, has been performed. Finally, as a conclusion,
some rules for selecting the most appropriate instruments for obtaining
the required information have been set up.
Materials and Methods
Reagents
and Solutions
For details of the reagents
and solutions used in the study, refer to the Supporting Information.
Colorimetric Reaction on
Solid Supports
For preparation
of the colorimetric solid supports used in the study, refer to the Supporting Information.
Analytical Response Measurements
Four different instruments
were used: UV–Vis diffuse reflectance spectrometer (Cary 60
UV–Vis, Agilent), UV–Vis portable reflectance spectrometer
(OceanOptics), smartphone, and smartphone coupled to a miniaturized
spectrometer (GoSpectro, Alphanov). Two different procedures were
used to obtain the RGB components: (i) nonprocessed images and (ii)
processed images.[30] For details of the
instrumentation used and the measurement of the analytical response,
refer to the Supporting Information.
Results and Discussion
Panel of Color Control and Colors of Monitoring
Sensors
A color palette covering the visible color range
(Figure S1) was selected as the validation
set. Besides, three
different solid supports (PDMS, nylon, and paper) on which chemical
reactions have been carried out have been selected as cases of study.
The first example was a NH4+ sensor, the second
one was a paper-based sensor employed to determine H2S
by forming methylene blue, and the last example was a plasmonic sensor
of H2S that used AgNPs retained on a nylon membrane. In Figure , images of the three
selected sensors (with and without exposure to the analyte) are shown;
it is evident that the formed colors were different and corresponded
to different spectral regions. All of these materials (paper, nylon,
and PDMS) allowed light to pass through, and so, the analytical signal
can be obtained using reflectance and transmittance modes.
Figure 1
Colorimetric
solid sensors using different supports (nylon, PDMS,
and paper) exposed at different concentrations (B: blank and S: sample).
Colorimetric
solid sensors using different supports (nylon, PDMS,
and paper) exposed at different concentrations (B: blank and S: sample).
Responses Using a Lab Reflectance Diffuse
Instrument as a Reference
Table shows the
characteristics evaluated for the lab equipment: some instrumental
properties; portability related to size, weight, and autonomy; and
cost and sustainability measured as carbon footprint according to
Pla-Tolós et al.[31] It has a spectral
resolution of 1.5 nm with the wavelength in the range of 190–1100
nm. The drawbacks of this instrument are lack of portability, its
cost, and a higher carbon footprint.
Table 1
Main Analytical
Properties of the
Different Types of Instruments Used
specifications
visual inspection naked eye
smartphone (digital image)
smartphone-miniaturized
spectrometer
portable reflectance spectrometer
lab reflectance spectrometer
analysis type
semiquantitative
quantitative
quantitative
quantitative
quantitative
spectral resolution
5 nm
0.5 nm
1.5 nm
spectral range
380–750 nm
190–1100 nm
190–1100 nm
light source
LED or halogen bulb
halogen, vis-NIR, (HL-2000-HP-FHSA,
Ocean Optics)
xenon flash lamp (80 Hz)
run time
5 s
2 s
20 s
30 s
CV (%)
<1.5
<1.5
<1
<1
light source power
10 W
20 W
9–18 W
operating system
android or iOS
android or iOS
size
50 × 20 × 20 mm
89 × 63.3 × 32 mm
550 × 420 × 270 mm
weight
30 g (just device)
265 g (just spectrometer)
20 kg
price
300–600 €
70–1200 €
8000–10000 €
9000–12000 €
sustainability (carbon
footprint)
0.0014 kg CO2
0.0014 kg CO2
0.024 kg CO2
0.17 kg CO2
To obtain quantitative analytical parameters
such as S/N noise
(calculated as X̅/s, standard deviation),[32] the spectra of the panel of 45 colors (Figure S1) were registered, considering colors
divided into five groups of nine components each. Figure shows the spectra obtained
by the lab instrument when different colors of the red range were
measured, as an example; the S/N value obtained was 34, as shown in Table . The table also shows
the % RSD obtained from n = 3 spectra registered
in the same working session and in different ones (n = 3). As can be seen, the inter- and intraday precisions were lower
than 2% for this instrument.
Figure 2
Reflectance spectra corresponding to different
colors obtained
using different instruments. (The absorption spectra for the smartphone-spectrometer
were obtained using GoSpectro (Alpahanov) coupled to a smartphone
at optimum conditions (sensor at 1 cm, halogen lamp, 20 W) in a wavelength
range from 350 to 700 nm; data was obtained using the GoSpectro App
developed by Alphanov. For the portable spectrometer, the absorption
spectra were obtained using a UV–vis portable reflectance spectrometer
(Ocean Optics), a tungsten halogen lamp of 20 W (HL-2000-HP-FHSA Light
Source from Ocean Optics), and data was registered using the computer
program OceanView).
Table 2
%RSD Inter-
and Intraday Deviations
for Different Colors at Different Wavelengthsa
(%RSD)
instrument
royal yellow
(460 nm)
fire red (495 nm)
light blue (590 nm)
apple
green (710 nm)
S/N
intraday/interday
intraday/interday
intraday/interday
intraday/interday
lab reflectance spectrometer
0.70/0.9
0.2/1.4
0.2/0.4
1.6/2.0
34
portable reflectance spectrometer
0.1/0.5
0.1/0.5
0.05/0.3
0.05/0.2
47
smartphone-spectrometer (reflectance mode)
1.5/1.6
0.4/2.2
0.8/1.2
0.3/1.6
18
Signal-to-noise (S/R) ratio for
different instruments. The S/R ratio is calculated as 5 × Standard
deviation/Δsignal
Reflectance spectra corresponding to different
colors obtained
using different instruments. (The absorption spectra for the smartphone-spectrometer
were obtained using GoSpectro (Alpahanov) coupled to a smartphone
at optimum conditions (sensor at 1 cm, halogen lamp, 20 W) in a wavelength
range from 350 to 700 nm; data was obtained using the GoSpectro App
developed by Alphanov. For the portable spectrometer, the absorption
spectra were obtained using a UV–vis portable reflectance spectrometer
(Ocean Optics), a tungsten halogen lamp of 20 W (HL-2000-HP-FHSA Light
Source from Ocean Optics), and data was registered using the computer
program OceanView).Signal-to-noise (S/R) ratio for
different instruments. The S/R ratio is calculated as 5 × Standard
deviation/Δsignal
Responses
with a Portable Reflectance Diffuse UV–Vis
Spectrometer
The instrument used in this work consisted of
a modular device constituted by a lamp, detector, fiber optic, integrating
sphere of 8 mm, and a computer. As can be seen in Table , from the instrumental point
of view, this instrument presents a very good resolution (<0.5
nm). The components can be set on a suitcase and easily transported,
as their weight (taking all of the components) is around 2 kg. The
price is lower than the conventional lab instrument with the diffuse
reflectance accessory. Regarding sustainability, the carbon footprint
is much lower than that of traditional equipment. In the case of conventional
lab instruments, the measuring methodology is very well established,
and the measuring conditions are usually not affected by environmental
conditions.When measurements were performed on the color palette
control, the spectra obtained using this instrument are similar to
those obtained by using the lab instrument (see Figure ). The highest precision was obtained using
the portable optical fiber reflectometer with lower values of % RSD.
A very good S/N value of 47 was also obtained.
Figure 3
Prototype of the spectrometer
adapted to a smartphone: (A) reflectance
mode and (B) transmission mode.
Prototype of the spectrometer
adapted to a smartphone: (A) reflectance
mode and (B) transmission mode.
Responses with a Smartphone Coupled to a Miniaturized Spectrometer:
Establishing Rules for Accurate Measurements
A smartphone,
coupled to a minispectrometer (GoSpectro) that uses the camera of
the phone as an optical sensor, was employed. GoSpectro is an app
for Android and iOS licensed by Alphanov, which allows light calibration
and spectra registration. To the best of our knowledge, this is the
first study where this instrument has been used for quantitative analysis.
The instrumental characteristics of this device are shown in Table It has a resolution
of 5 nm and an optical entrance of 0.6 mm; the optical entrance parameter
determines the size of the sample to be measured and the position
of the device regarding the sample. It can measure in reflectance
or transmittance mode (depending on whether the material is transparent
or translucent), depending on whether the light is reflected off the
sample or light is going through the sample. Besides, it can be connected
to a fiber optic to have more precise measurements. As it has a small
size and low weight, it is suitable for in situ analysis. Therefore,
as can be seen in Table , the carbon footprint is lower than the other compared instruments.
The cost of this instrument is very low. The appropriate data acquisition
with the minispectrometer-smartphone devices requires controlling
the parameters of the instrument (calibration) and other external
parameters, such as light, sample position, or the type of mobile
phone employed. This instrument is easily calibrated; however, one
of the main drawbacks is that the user needs to control carefully
the environmental conditions, such as light. This is a common problem
for all of these types of instruments due to light affecting the color
responses.[33]Regarding the position
of the instrument, it was concluded that a better way to obtain precise
results was to fix the instrument (spectrometer) 90° with respect
to the horizontal surface (Figure A), while the smartphone was placed horizontally. This
position guarantees that the distance between the sample and the spectrometer
device is the same all over the sample. The distance to the sample
was dependent on the sample size. It was observed that the smaller
the area of the sample, the closer the spectrometer device should
be placed. For round samples of 1 cm diameter, the optimum distance
of the spectrometer end to the sample was 1 cm, while the distance
of the smartphone from the surface was 5 cm. The environmental light
should also be controlled to perform the measurement. Thus, the sample
spectra were registered when different lights were used (environmental
light like sunlight as a natural source and fluorescent tubes (50
W) and light from a LED (5 W) or a halogen bulb (10 W) located at
10 cm from the sensor (Figure S2A)). The
sunlight spectrum is more uniformly distributed and more sensitive;
however, the signal precision was poor due to its dependence on the
time of the day or the weather. The use of a fluorescent tube was
not recommended because of its poor intensity and smaller range of
lighting wavelengths. Although the LED bulb provided good results
and a wide range of wavelengths, we propose the use of a halogen bulb
because it provides higher sensitivity (Figure S2B). In order to perform the measurements in transmission
mode, a homemade sample holder was used. It consists of a cylindrical
plastic piece with a small hole that would be fixed at the extreme
of the spectrometer. The sample is introduced at the base of the cylindrical
piece and will be in between both the pieces (the plastic piece and
the spectrometer) (Figure B).Another problem of using a smartphone as an analytical
instrument
is the uncertainty in reproducibility across smartphone devices.[34] The effect on the signals when using different
smartphones (three different iPhone models) was tested by registering
the spectra of four paper colors (red, gray, blue, and green). As
can be seen in Figure S3, the shape of
the spectra obtained are quite similar to each other; however, the
absorbance value was dependent on the model phone. Based on these
results, we can conclude that the calibration and the sample measurements
should be done with the same smartphone device to obtain reproducible
signals under controlled light conditions, position, and size of the
sample.By working under optimal experimental conditions, the
reflectance
spectra of the palette of 45 colors were registered. As can be seen
(Figure ), similar
analytical signals were obtained using the reflectance instruments;
however, slightly lower absorbance signals were obtained when a smartphone-spectrometer
device was used. A slight shift in the maximum absorption can be observed
when using the smartphone coupled to a spectrometer. These results
are satisfactory, and this displacement can be explained by different
spectral resolutions of different instruments. Although the values
of intraday precision were higher than those given by the other instruments,
these results were approximated (<10%) (Table ). As expected, the S/N ratio was also lower
than those of the other instruments compared.By using this
instrument, the raw data obtained corresponds to
the light intensity. These data should be converted to absorbance
values. Therefore, we will need to register the blank signal (blank
material) in order to obtain the Io and
the I values of the different samples. These data
will be processed in order to obtain the absorbance from the transmittance
using the Lambert–Beer law (Figure A). From the analytical point of view, there
is a need to calculate the concentration using standards and their
absorbance. In this case, there are two different ways to calculate
it when using this prototype: (i) by exporting and processing the
raw spectral data to external programs such as excel or (ii) by using
an app designed for direct calculation. The app for spectrometer-smartphone
software (app) has many advantages such as it is quicker, and the
data can be stored and easily transferred via Wi-Fi. In this sense,
a calculation option was included in the GoSpectro App from the MINTOTA
research group. By clicking the calculation button, the concentration
of the sample is calculated using the spectral data of the blank,
two standards of known concentration, and the sample. Thus, the user
will only need to measure the blank, two standards, and the sample.
Calibration of one point will be used as a calibration model for each
standard, in which a K constant = standard concentration
1/(Abs standard 1 – Abs blank sensor) will be calculated and
used to calculate the concentration of the sample (C sample = (Abs sample – Abs blank sensor)/K constant) for both standards. Figure shows some images of the different screens of the
app. The app has the option to select up to five wavelengths for calculating
the concentration and two standards for calibration.
Figure 4
Schematic illustration
of a sensor measurement using (A) a smartphone-spectrometer
device and recording of the spectra. (B) Digitalized image using a
smartphone camera and determination of the RGB parameters.
Figure 5
App for calculating the concentration of a sample using the spectra.
Schematic illustration
of a sensor measurement using (A) a smartphone-spectrometer
device and recording of the spectra. (B) Digitalized image using a
smartphone camera and determination of the RGB parameters.App for calculating the concentration of a sample using the spectra.
Response with Smartphone and RGB Color Coordinates:
Establishing
Rules
A smartphone can also be used to obtain digital images
in order to obtain the color coordinates, and RGB is one of the most
commonly used color models in image processing (Figure B). However, color can be converted to other
models such as hue, saturation, and value (HSV); hue, saturation,
and lightness (HSL); hue, saturation, and intensity (HSI); and lightness,
green-red, and blue-yellow (L*a*b*). These values can be correlated with the analyte concentrations.[35] The smartphone cameras have mostly limited control
of camera parameters (e.g., exposure time, shutter speed, ISO, and
color balance, and no access to raw image data), and the image processing
is applied automatically and varies significantly across smartphones.
These methods disturb the linearity of the pixel intensity values,
which causes loss of information. On the other hand, ambient light
conditions are difficult to control during imaging in uncontrolled
environments.The mobile phone can be set in the same conditions
described previously for reflectance mode or using the protocol developed
by Pla-Tolos et al.[36] which used a box
and artificial light for controlling the light conditions. The digitalized
images obtained (JPEJ format) can be processed by external programs
such as GIMP, Jimage or MATLAB in order to obtain the color components.
Besides that, commercial apps, such as Color Grab* for android and
color Assist for iOS, allows easily to obtain the color coordinates.
These data can be used for prediction by using multivariate methods[37] or by correlation one component[36] or the ratio between two components with the analyte concentration.[38]Using the conditions established previously
and using a commercial
app (Color Assist), the RGB components of the palette of 45 colors
were obtained. The precision obtained was 4.0/3.9 for intra- and interday
(n = 3), respectively, for a blue color as an example.
Conditions such as light source, mobile and sample position, and smartphone
used have to be considered to obtain reproducible signals. This problem
can be reduced if images of the calibration points and the samples
are taken at the same time as discussed in Analytical
Response Measurements section.Here, an app that allows
calculating the concentration from the
RGB of the image has also been developed (Figure ). In order to determine the concentration
in a sample, the user will need photos of the blank signal, a standard
with a known concentration, and the sample with an unknown concentration,
all at the same time. Using the calibration of one point as a calibration
model, the app can calculate the sample concentration. By performing
the assay under these conditions, we will guarantee that the environmental
measurement conditions are equal for all of the points measured. The
app will obtain the values of RGB for the blank, the standard, and
the sample, and the concentration of the sample will be calculated
using the three RGB components.
Figure 6
App for calculating the concentration
of a sample using the RBG
components.
App for calculating the concentration
of a sample using the RBG
components.As can be seen in Table , the use of the smartphone-free
spectrophotometer is one
of the simpler instruments. This is a very economic option (nowadays
everybody has a smartphone) and the cost to download the app is not
very high.Other aspects considered were the analytical data
provided by different
instruments and its conversion into analytical information. Multivariate
methods were used to analyze the information provided using the spectral
data and the RGB components (see the Supporting Information). The RBG univariate models present a lack of selectivity
and do not have enough selectivity to establish differences between
very similar colors. Small color changes cannot be detected in the
analysis, as the red, green, and blue (RGB) intensity values may not
be sufficient. These aforementioned concerns make smartphones limited
for full applicability to quantitative analysis.
Responses by
Visual Inspection
A color change observable
by the naked eye in response to the concentration of an analyte can
be an indication of a problem warranting further attention. This type
of methodology is very useful for qualitative or semiquantitative
analysis. To estimate the concentration by visual inspection, the
user will need a cart of colors corresponding to different concentrations
and the sample. Although this methodology was proposed for strip reagents
in the 1960s, it is still very useful.[39] Its limitations for quantitation, selectivity, accuracy, and precision
should be considered, yet it can be useful in several situations and
fields.
Solid Chemosensors as a Case Study: Scaling the Information
The aim of this section is to establish some guidelines to select
the appropriate measuring instrument for an analysis depending on
the demanded information. Traditionally, this selection has been made
mainly on some analytical properties but, nowadays, other ones should
also be considered. Different instruments already evaluated have been
used to obtain the analytical responses of the three sensors exposed
at different analyte concentrations. As an example, Figure shows the spectra of the H2S sensor based on the formation of methylene blue. The spectral
shape obtained using the reflection mode was similar for all of the
instruments, although the absorbance values were slightly lower for
a smartphone-spectrometer. However, by measuring in the transmission
mode, the absorbance values were a bit higher than those obtained
in the reflectance mode. Similar results were obtained for the other
sensors tested.
Figure 7
Spectra corresponding to H2S paper sensors
using methylene
blue reaction using different instruments.
Spectra corresponding to H2S paper sensors
using methylene
blue reaction using different instruments.The figures of merit of different sensors using different instruments
are shown in Table . For all sensors, the analyte quantitation was carried out by external
calibration. The limits of detection (LODs) and limits of quantification
(LOQs) were calculated as 3sa/b1 and 10sa/b1, respectively, where sa and b1 are the standard deviations
of the ordinate and the slope of the regression. The linear range,
sensitivity, and precision of the methods were evaluated. The figures
of merit of different sensors using portable instruments are similar
to those obtained using the traditional lab instrument. Good correlations,
appropriate detection, and quantification limits were obtained. In
general, for the three sensors, slightly higher LODs and LOQs were
obtained with a smartphone-spectrometer. On the other hand, good results
were also obtained using the RGB components from the images. As can
be seen, depending on the sensor, the RGB selected were different: R (Red) component for the NH3 sensor, R (Red) for the H2S sensor (in paper), and G (Green) for H2S (in nylon). In this case, the
ImageJ program was used. From Table , it can be seen that when images were processed the
analytical parameters improved slightly. In all cases, a good correlation
was obtained and the analytical parameters were similar to those obtained
with other instruments (lab or portable reflectance instrument).
Table 3
Figures of Merit of the Sensors of
PDMS, Nylon, and Paper Using Different Instruments and Signals (Absorbance
or RGB Components)
In order to evaluate the accuracy and precision, several
standards
of known concentration were used as samples. Table shows the concentrations obtained at two
different concentration levels, and the relative errors corresponding
to the use of different instruments for the two sensors assayed at
ppm levels. Good results were obtained for all instruments. Similar
results were obtained for the H2S sensor of nylon at ppb
levels, as can be seen in Figure . It is also observed that the concentrations obtained
using the developed app were comparable to those calculated by the
external data treatment with a smartphone-spectrometer, portable reflectance
instrument, or laboratory reflectance instrument.
Table 4
Concentrations of H2S in
Solution and Relative Errors Obtained Using Different Instruments
sample 1: 4.5 mg/L
sample 2: 7 mg/L
lab reflectance diffuse
spectrometer
4.68 ± 0.08
6.70 ± 0.07
Er = 4.0%
Er = −4.3%
RSD% = 1.7
RSD% = 1.0
portable spectrometer
4.48 ± 0.08
6.70 ± 0.04
Er = −0.4%
Er = −4,3%
RSD% = 1.8
RSD% = 0.6
smartphone-spectrometera
4.32 ± 0.14
6.71 ± 0.05
Er = −4.0%
Er = −4.14%
RSD% = 3.2
RSD% = 0.7
smartphone-spectrometerb
4.64 ± 0.12
6.8±
0.3
Er = 3.2%
Er = −2.8%
RSD% = 2.4
RSD% = 3.9
smartphone-digital images (RGB)a (R component)
4.34 ± 0.09
7.1 ± 0.2
Er = −3.6%
Er = 1.4%
RSD% = 2.0
RSD% = 2.8
smartphone-digital images (RGB)b (R component)
4.6 ± 0.3
7.3 ± 0.4
Er = 4.0%
Er = 1.2%
RSD% = 4.8
RSD% = 2.7
Using external data programs (Excel).
Using GoSpectra or spectrofree calculation
app.
Figure 8
Concentration of H2S (H2S–nylon sensor
with AgNPs) obtained using different instruments. (a) Smartphone-spectrometer
in reflectance mode; (b) portable reflectance instrument; (c) laboratory
reflectance instrument; (d) smartphone-spectrometer in transmission
mode and different strategies for calculation. * Using the app designed
for the smartphone-minispectra and the app for smartphone-spectrofree.
Concentration of H2S (H2S–nylon sensor
with AgNPs) obtained using different instruments. (a) Smartphone-spectrometer
in reflectance mode; (b) portable reflectance instrument; (c) laboratory
reflectance instrument; (d) smartphone-spectrometer in transmission
mode and different strategies for calculation. * Using the app designed
for the smartphone-minispectra and the app for smartphone-spectrofree.Using external data programs (Excel).Using GoSpectra or spectrofree calculation
app.Based on the information
provided in Table S1, it can be seen that the tested analytes are important in
different fields, and in some cases, the concentration levels are
regulated.
If analytical characteristics of smartphone methodologies are compared
to others employing instruments, it can be seen that these options
are the cheapest and the easiest for in situ analysis. They are also
the most sustainable. The use of lab and portable reflectance instruments
are always a good choice if accuracy and precise results are required
or even for validation studies of the other instruments. Although
the smartphone requires strict control of the environmental conditions
(light source, mobile position, mobile model, sample size), the operation
is very simple. A nonspecialized person can carry it out by following
a protocol. The use of smartphones has the advantages of portability,
computing power, memory, capability to connect to other IT systems,
and the signal or captured images can be transmitted to a custom-designed
app for being processed using an appropriate algorithm, which allows
obtaining the concentration. Although a smartphone is the best selection
for analysis in situ, it can also be used as a lab instrument if a
fast analysis and/or cheap analysis is required.
Conclusions
In this paper, the analytical information given by different types
of instruments was scaled, and the main advantages and drawbacks of
several instruments that can be used to measure color on the surface
are discussed. Instruments such as a reflectance lab instrument, a
reflectance portable instrument, and a smartphone (as an image grabber
or coupled to a minispectrometer) have been compared from different
points of view, such as analytical and environmental, among others.
As a case study, the color developed on three solid chemosensors made
of different materials, paper, PDMS, or nylon, has been tested. The
figures of merit—linearity, LODs, LQDs, precision, and accuracy—obtained
using lab instruments are slightly better than using a smartphone.
In the case of using a smartphone, as long as the measurement conditions
(light source, mobile phone position, model, sample size) are controlled,
the measurements obtained will be suitable; in this sense, here some
rules have been established. When we use the smartphone-spectrometer
option, more precise results can be obtained using a fiber optic to
capture the light. The achieved results indicate that the smartphone
is a good alternative for in situ analysis or for fast and/or cheap
analysis, either using the RGB coordinates from images, which can
be processed in order to improve the values of coordinates, or obtaining
the spectra; the latter option improves selectivity. On the other
hand, the use of smartphone has the advantages of having an app to
easily obtain raw data and directly transform them into concentrations,
as demonstrated here, and the results can be easily stored and/or
transferred and it allows one to make a quick decision for solving
a given problem if necessary. On the other hand, lab instruments involve
a higher carbon footprint than portable instruments and smartphones.
Hence, portable instruments have been shown to be a suitable, economic,
and environmentally friendly alternative for in situ analysis.
Authors: Zoya Volynskaya; Abigail S Haka; Kate L Bechtel; Maryann Fitzmaurice; Robert Shenk; Nancy Wang; Jon Nazemi; Ramachandra R Dasari; Michael S Feld Journal: J Biomed Opt Date: 2008 Mar-Apr Impact factor: 3.170
Authors: Sandeep Kumar Vashist; Thomas van Oordt; E Marion Schneider; Roland Zengerle; Felix von Stetten; John H T Luong Journal: Biosens Bioelectron Date: 2014-08-19 Impact factor: 10.618
Authors: J Pla-Tolós; P Serra-Mora; L Hakobyan; C Molins-Legua; Y Moliner-Martinez; P Campins-Falcó Journal: Sci Total Environ Date: 2016-07-01 Impact factor: 7.963
Authors: Andrew J S McGonigle; Thomas C Wilkes; Tom D Pering; Jon R Willmott; Joseph M Cook; Forrest M Mims; Alfio V Parisi Journal: Sensors (Basel) Date: 2018-01-14 Impact factor: 3.576