A Dye-Assisted Paper-Based Assay to Rapidly Differentiate the Stress of Chlorophenols and Heavy Metals on Enterococcus faecalis and Escherichia coli

Biological toxicity testing plays an essential role in identifying the possible negative effects induced by substances such as organic pollutants or heavy metals. As an alternative to conventional methods of toxicity detection, paper-based analytical device (PAD) offers advantages in terms of convenience, quick results, environmental friendliness, and cost-effectiveness. However, detecting the toxicity of both organic pollutants and heavy metals is challenging for a PAD. Here, we show the evaluation of biotoxicity testing for chlorophenols (pentachlorophenol, 2,4-dichlorophenol, and 4-chlorophenol) and heavy metals (Cu2+, Zn2+, and Pb2+) by a resazurin-integrated PAD. The results were achieved by observing the colourimetric response of bacteria (Enterococcus faecalis and Escherichia coli) to resazurin reduction on the PAD. The toxicity responses of E. faecalis-PAD and E. coli-PAD to chlorophenols and heavy metals can be read within 10 min and 40 min, respectively. Compared to the traditional growth inhibition experiments for toxicity measuring which takes at least 3 h, the resazurin-integrated PAD can recognize toxicity differences between studied chlorophenols and between studied heavy metals within 40 min.


Introduction
Persistent organic pollutants (POPs) are chemicals of global concern due to their unique combination of physical and chemical properties as well as their significant negative effects on human health and the environment [1]. They exist in a stable state with high lipid solubility [2,3], leading to their accumulation and the subsequent accumulation of toxicity [2,4]. Heavy metal in the environment is also of concern due to its non-degradability and accumulation in water [5]. Exposure to both POPs and heavy metals is considered serious a health risk [6]. Hence, detecting the toxicity of such substances in the environment quickly and accurately is critical to assess their risk.
There are various conventional analytical techniques for the detection of organic and heavy metal pollutants, such as High-performance liquid chromatography (HPLC), Gas chromatography (GC), atomic absorption spectroscopy (AAS), mass spectrometry (MS), etc. These analytical techniques are limited by the investment costs, the necessity of skilled labor during operation, sample pre-processing, and lack of real-time capability [7]. Paper is a versatile and cost-effective medium that is easy to transport. The advent of microfluidic paper-based analytical devices (PADs) can simultaneously satisfy on-site detection while requiring fewer samples, providing ease of operation and requiring no external power, labor during operation, sample pre-processing, and lack of real-time capability [7]. Paper is a versatile and cost-effective medium that is easy to transport. The advent of microfluidic paper-based analytical devices (PADs) can simultaneously satisfy on-site detection while requiring fewer samples, providing ease of operation and requiring no external power, making these devices increasingly useful in biomedicine [8], environmental testing [9,10], and food safety [11]. The integration of colourimetric detection with PAD is one of the most used detection methods due to its visibility, excellent stability, rapid detection capabilities, and ease of use in the field. Various colorimetric PAD assays have been reported, with the change in color of the PAD before and after the test. The Griess reagent was used to integrate into the PAD, which then combined with nitrite to produce an azo dye, visible as a magenta hue [10]. To detect heavy metal ions such as Ni (II), Cr (VI), and Cu (II) in water samples, color alterations before and after the indicator-metal complex system were utilized [12,13]. The utilization of silver nanoparticles in conjunction with PAD devices has been demonstrated as a viable method for detecting cyanide (CN) in water samples. This was achieved by monitoring the color alteration of silver nanoparticles-PAD from yellow to colorless [14]. In addition, gold nanoparticles were also reported to be used in the colorimetric PADs in conjunction with digital images to measure color responserepresenting additional advantage [15].
Resazurin is commonly used as an oxidation−reduction indicator, formulated into in vitro toxicology assay kits (i.e., AlamarBlue). The reduction in blue resazurin to pink resorufin, then further to colorless dihydroresorufin (resazurin→resorufin ⇄ dihydroresorufin) is the response to intercellular metabolic activity [16]. Therefore, it is widely used as an indicator of microbial growth and antibacterial properties [17,18], antibiotic susceptibility testing [16], and cytotoxicity [19][20][21]. A microfluidic droplet reactor with resazurin reduction assay has been utilized to detect heavy metals [22,23] and hydrophobic toxicants [24] that inhibit E. faecalis metabolism. However, the microfluidics system is not portable and requires exterior force to drive the liquid. As a solution to these limitations, in this present study, resazurin reduction assay was integrated with PAD devices to differentiate the biotoxicity of chlorophenols (pentachlorophenol (PCP), 2,4-dichlorophenol (2,4-DCP), 4-chlorophenol (4-CP)) and heavy metals (Pb 2+ , Zn 2+ , and Cu 2+ ) on E. coli and E. faecalis. The kinetics of color change in resazurin on PAD captured by a smartphone was used to measure the bio-toxicity of studied substances. By comparing these results to the traditional biotoxicity measures, we proposed that PAD integrating resazurin reduction assay is a novel and efficient method to study the stress of toxicants on microorganisms.

Fabrication of PADs
WCP used in this experiment was sliced into strips at the size of 3 × 50 mm. The strips were soaked in 0.2 mM resazurin solution for 10 min and then placed in a glass petri dish with a lid and allowed to air dry overnight in a fume hood under aphotic and ambient conditions. The dry WCP strips were stored in a desiccator for later use as resazurin-integrated PADs. dihydroresorufin) is the response to intercellular metabolic activity [16]. Therefore, it is widely used as an indicator of microbial growth and antibacterial properties [17,18], antibiotic susceptibility testing [16], and cytotoxicity [19][20][21]. A microfluidic droplet reactor with resazurin reduction assay has been utilized to detect heavy metals [22,23] and hydrophobic toxicants [24] that inhibit E. faecalis metabolism. However, the microfluidics system is not portable and requires exterior force to drive the liquid. As a solution to these limitations, in this present study, resazurin reduction assay was integrated with PAD devices to differentiate the biotoxicity of chlorophenols (pentachlorophenol (PCP), 2,4-dichlorophenol (2,4-DCP), 4-chlorophenol (4-CP)) and heavy metals (Pb 2+ , Zn 2+ , and Cu 2+ ) on E. coli and E. faecalis. The kinetics of color change in resazurin on PAD captured by a smartphone was used to measure the bio-toxicity of studied substances. By comparing these results to the traditional biotoxicity measures, we proposed that PAD integrating resazurin reduction assay is a novel and efficient method to study the stress of toxicants on microorganisms.

Fabrication of PADs
WCP used in this experiment was sliced into strips at the size of 3 × 50 mm. The strips were soaked in 0.2 mM resazurin solution for 10 min and then placed in a glass petri dish with a lid and allowed to air dry overnight in a fume hood under aphotic and ambient conditions. The dry WCP strips were stored in a desiccator for later use as resazurin-integrated PADs.

PAD Toxicity Detection Method and Data Analysis
Three types of chlorophenols, PCP, 2,4-DCP, and 4-CP, were spiked in the bacterial culture prepared in Section 2.3 to yield final concentrations of 10 mg/L, respectively. Thirty µL chlorophenol-spiked bacterial culture at OD 600nm of 1.4, 0.85, and 0.45 was, respectively, dropped onto PADs prepared in Section 2.2. A smartphone was used to record the color changes on the PAD. Meanwhile, a positive control group with bacterial culture without toxicants addition was set up and a blank control only with BHI was also set up. Every 10 min, photos were snapped in the recorded video and then imported into the application Color Picker to quantify the hue value. The increment of the hue value (∆Hue) was obtained by subtracting the initial hue value (time = 0 min).
The kinetic reduction equation for resazurin was the basis for this experiment. It is used as a toxicity indicator when comparing the toxicity of toxic substances with E. coli. The reduction in resazurin by living cells: here represent reducing substances such as NADH/NADPH in the living cells). The colorimetric based on resazurin used as a toxicity indicator when comparing the toxicity of toxic substances with E. coli and can be described by Equation (1) [25,26]: The value of k 1 and k 2 can be obtained by fitting chromaticity values to the reaction reduction Equation (1).

Applicability for Heavy Metal Toxicity Detection
To verify the feasibility of this PAD technique in the detection of heavy metal toxicity, copper, zinc, and lead were chosen as proxies, whose concentrations were determined according to IC 50 values published in literatures [27][28][29]. The copper (II) sulphate pentahydrate, zinc (II) acetate, and lead (II) nitrate solutions were spiked in the bacterial culture with final metal ion concentrations of 7.00, 10.00, and 18.00 mg/L, respectively. Thirty µL metal-spiked bacterial culture was dropped onto the resazurin-integrated PAD prepared in Section 2.3. Two groups of control were set up and the same experiment was carried out in the same way as that mentioned in Section 2.4.

Traditional Toxicity Detection
To evaluate the biotoxicity test PAD, a traditional growth curve method was conducted in BHI broth to confirm the toxicity of chlorophenols, and heavy metals used above at the relevant concentrations, in which another 0.4 mL of subcultured bacteria (E. faecalis and E. coli, respectively) was mixed with sterile BHI broth in 100 mL serum bottles. Chlorophenols and heavy metals were then spiked, respectively, to result in the concentrations used above. Positive controls were also conducted. Serum vials were sealed, and they were incubated at 37 • C. OD 600nm was monitored until it reached the stationary phase at regular intervals.

Results and Discussion
Both E. faecalis (Gram-positive) and E. coli (Gram-negative) were common facultative anaerobic bacteria inhabiting the human gastrointestinal tract, and their isolation and culture were frequently used as indicators of bacterial toxicity [30]. The videos of resazurin reduced by E. faecalis and E. coli on the PAD were sped up by a factor of 600 (details can be found in Videos S1-S4). As the bacterial culture solution was dripped onto the paper strip, the color changed from blue to pink, meaning the bacteria reduced resazurin to resorufin. Furthermore, the color changed at different rates under certain conditions, such as different species of bacteria, bacterial densities, etc.

The Kinetics of Color Change on PADs
The pictures captured in the recorded video to illustrate the color change in reducing resazurin by E. faecalis and E. coli ( Figure 1). The difference in hue values every ten 10 from those at 0 min were fitted in conjunction with Equation (1) (Figure 2). Table 1 summarizes the simulation results (k 1 and k 2 ). The majority of E. faecalis fitting results were more than 0.9 (>0.636, critical R 2 under p = 0.01). In general, the fitting outcomes for E. coli were higher than 0.9, which is higher than 0.467 (critical R 2 under p = 0.01). These results suggest that the model (Equation (1)) can reasonably be used to simulate the reduction process of resazurin on PADs for two different strains of bacteria, E. faecalis and E. coli.  For the E. coli on the right, the D1 and D2 marks represent that E. coli was diluted 2 and 4 times, respectively, and the OD600nm corresponds to 0.85 and 0.45. In addition, the petri dish labeled with E. coli represents undiluted bacteria).

For Bacterial Species
Two strains of bacteria under different densities were tested for their ability to reduce resazurin on the PAD. It can be seen in Figure 2a-c that the color change in positive control (E. faecalis with BHI) reaches equilibrium at about 30 min, indicating that resorufin has reached its maximum concentration in the E. faecalis system. For E. coli, the ∆Hue value of the positive control showed an increasing trend during the detection time (Figure 2d-f), indicating that resazurin was still being reduced in E. coli system. The reduction in resazurin requires attachment to bacteria, diffusion through cell walls and membranes, and intracellular metabolism [31]. It can also be seen in Table 1 that the k 1 value of E. faecalis fitted with different bacterial densities was between 0.35 and 0.59, while that of E. coli was 0.0037-0.041, revealing faster kinetics of resazurin reduction by E. faecalis than by E. coli.
It is believed that Gram-positive bacteria have monolayer cell walls that are composed primarily of peptidoglycan and acidic polysaccharides, such as teichoic acid. Gram-negative bacteria contain multilayered cell walls and lipopolysaccharide (LPS)-containing outer membrane [32]. The presence of large numbers of LPS makes the cell membrane less permeable, resulting in slowing down the diffusion of dye into the cells [33]. It was reported that resazurin was reduced to resazurin within the bacteria [34]. By adsorbing resazurin to the bacteria, resazurin passes through the cell wall and membrane, then reacts with intracellular metabolites [26]. According to Equation (1), [M] represents the reducing substance, such as NADH and NADPH, in living bacteria. The content of resazurin (meaning of ∆Hue 0 ) that enters the bacteria through the bacterial membrane is relatively fixed due to the limited absorption sites on the bacterial membrane [26]. Because of the different bacterial structures of E. faecalis and E. coli, the content of resazurin entering the bacteria will be different due to the difference in the speed of resazurin passing through the bacterial cell wall/membrane. The kinetics under the same bacterial density (positive control fitting curve, the red one, in Figure 2) and the simulated k 1 value demonstrate that E. faecalis reduces resazurin faster than E. coli.

For Bacterial Density
The simulated k 1 values based on Figure 2 are summarized in Table 1. E. faecalis density at OD 600nm 1.4 and 0.85 had the k 1 value of 0.059 and 0.050 min −1 , respectively. Although these two densities were different, the amount of bacteria in the culture medium remained in the same order of magnitude (~10 8 ), resulting in nonsignificant resazurin reduction kinetics difference between them. When the bacterial culture was further diluted (four times) to achieve density at OD 600nm 0.45, the resazurin reduction kinetics significantly slowed down (k 1 at 0.035 min −1 ). The same phenomenon manifested in both the control and chlorophenol-treated groups (Figure 2a-c), whose statistical analysis results are shown in Figure 3a. Although the addition of chlorophenols impacted E. faecalis and its reducing resazurin on PAD at densities of 1.4 and 0.85, it was unable to identify chlorophenols' toxicity difference. Meanwhile, when E. faecalis density was at 0.45, according to the fitted k 1 value in Table 1 and statistical analysis in Figure 3a, the toxicity of the three chlorophenols could be sorted as PCP > 2,4-DCP > 4-CP, which was closely correlated with the number of substituted chlorine atoms [35] and the same as the toxicity sequence of various chlorophenols [36]. Hence, OD 600nm 0.45 was recommended as E. faecalis density for further study. substance, such as NADH and NADPH, in living bacteria. The content of resazurin (meaning of ∆Hue0) that enters the bacteria through the bacterial membrane is relatively fixed due to the limited absorption sites on the bacterial membrane [26]. Because of the different bacterial structures of E. faecalis and E. coli, the content of resazurin entering the bacteria will be different due to the difference in the speed of resazurin passing through the bacterial cell wall/membrane. The kinetics under the same bacterial density (positive control fitting curve, the red one, in Figure 2) and the simulated k1 value demonstrate that E. faecalis reduces resazurin faster than E. coli.

For Bacterial Density
The simulated k1 values based on Figure 2 are summarized in Table 1. E. faecalis density at OD600nm 1.4 and 0.85 had the k1 value of 0.059 and 0.050 min −1 , respectively. Although these two densities were different, the amount of bacteria in the culture medium remained in the same order of magnitude (~10 8 ), resulting in nonsignificant resazurin reduction kinetics difference between them. When the bacterial culture was further diluted (four times) to achieve density at OD600nm 0.45, the resazurin reduction kinetics significantly slowed down (k1 at 0.035 min −1 ). The same phenomenon manifested in both the control and chlorophenol-treated groups (Figure 2a-c), whose statistical analysis results are shown in Figure 3a. Although the addition of chlorophenols impacted E. faecalis and its reducing resazurin on PAD at densities of 1.4 and 0.85, it was unable to identify chlorophenols' toxicity difference. Meanwhile, when E. faecalis density was at 0.45, according to the fitted k1 value in Table 1 and statistical analysis in Figure 3a, the toxicity of the three chlorophenols could be sorted as PCP > 2,4-DCP > 4-CP, which was closely correlated with the number of substituted chlorine atoms [35] and the same as the toxicity sequence of various chlorophenols [36]. Hence, OD600nm 0.45 was recommended as E. faecalis density for further study. The k1 values of resazurin reduction on E. faecalis-PADs and their differences were analyzed, and (b) the k1 values of resazurin reduction on E. coli-PADs and their differences were analyzed. D0 represents undiluted bacterial density, D1 represents bacterial density diluted twice, OD600nm = 0.85, and D2 represents a 4-fold dilution of bacterial density, OD600nm = 0.45. In addition, the ANOVA's turkey test was applied to variance analysis (* p < 0.05, ** p < 0.01, *** p < 0.001 compared in groups with the same dilution).
Compared with E. faecalis, the color changed slowly as different densities of E. coli were dripped onto PADs. According to the process of resazurin reduced by E. coli ( Figure  2d-f), the corresponding fitted k1 value in Table 1 and statistical analysis in Figure 3b, E. coli density at 1.4 and 0.85 did not make resazurin reduction kinetics significant among PCP, 2,4-DCP, and 4-CP. When E. coli density was at 0.45, the same as that of E. faecalis, the toxicity of those three chlorophenols was differentiated. However, this process required at least 80 min, which is longer than that required for E. faecalis system (i.e., 30 coli-PADs and their differences were analyzed. D0 represents undiluted bacterial density, D1 represents bacterial density diluted twice, OD 600nm = 0.85, and D2 represents a 4-fold dilution of bacterial density, OD 600nm = 0.45. In addition, the ANOVA's turkey test was applied to variance analysis (* p < 0.05, ** p < 0.01, *** p < 0.001 compared in groups with the same dilution).
Compared with E. faecalis, the color changed slowly as different densities of E. coli were dripped onto PADs. According to the process of resazurin reduced by E. coli (Figure 2d-f),  Table 1 and statistical analysis in Figure 3b, E. coli density at 1.4 and 0.85 did not make resazurin reduction kinetics significant among PCP, 2,4-DCP, and 4-CP. When E. coli density was at 0.45, the same as that of E. faecalis, the toxicity of those three chlorophenols was differentiated. However, this process required at least 80 min, which is longer than that required for E. faecalis system (i.e., 30 min). Therefore, OD 600nm 0.45 was used as the bacterial density for subsequent E. coli detection of heavy metal toxicity. It showed sensitivity as two different types of bacteria were diluted four-fold to show a difference in toxicity instead of an order of magnitude dilution in traditional measurement.

Comparison with Traditional Toxicity Detection Methods
Incubated with 10 mg/L PCP, the growth of Gram-positive E. faecalis was obviously affected (Figure 4a), indicating that the bacteria cannot grow. However, 10 mg/L of 2,4-DCP and 4-CP did not show an effect on the growth of E. faecalis. The traditional absorbance measurements cannot completely differentiate the toxicity of 10 mg/L PCP, 2,4-DCP, and 4-CP. Meanwhile, by the PADs developed in this present study, the inhibition of 10 mg/L PCP, 2,4-DCP, and 4-CP can be differentiated in 30 min.
Biosensors 2023, 13, x FOR PEER REVIEW 9 of 14 min). Therefore, OD600nm 0.45 was used as the bacterial density for subsequent E. coli detection of heavy metal toxicity. It showed sensitivity as two different types of bacteria were diluted four-fold to show a difference in toxicity instead of an order of magnitude dilution in traditional measurement.

Comparison with Traditional Toxicity Detection Methods
Incubated with 10 mg/L PCP, the growth of Gram-positive E. faecalis was obviously affected (Figure 4a  For Gram-negative E. coli, compared with the control group, the growth curve of 10 mg/L PCP showed a certain inhibitory effect (Figure 4b). Unlike what happened with E. faecalis, PCP partially inhibited the growth of E. coli, revealing E. coli resistance to potentially toxic substances. In contrast to the conventional method, which requires 4 h to demonstrate chlorophenol impact on E. coli growth, resazurin-integrated PADs can demonstrate chlorophenol inhibition effect on this Gram-positive strain in 80 min.

Toxicity Testing for Heavy Metals
The toxic effects of heavy metals on both E. faecalis and E. coli were detected by the resazurin-integrated PADs developed above at an OD600nm 0.45. According to the color change on PADs (Figure 5), the obtained data (ΔHue) were fitted to Equation (1). The simulation results (k1 and k2 values) were summarized in Table 2. The R 2 of E. faecalis fitting results were more than 0.97 (>0.636, critical R 2 ) and the R 2 of E. coli fitting results were around 0.9 (>0.467, critical R 2 ). This suggested that the model (Equation (1) can still well reflect the resazurin reduction process carried out by E. faecalis and E. coli on PADs in the presence of heavy metals. For Gram-negative E. coli, compared with the control group, the growth curve of 10 mg/L PCP showed a certain inhibitory effect (Figure 4b). Unlike what happened with E. faecalis, PCP partially inhibited the growth of E. coli, revealing E. coli resistance to potentially toxic substances. In contrast to the conventional method, which requires 4 h to demonstrate chlorophenol impact on E. coli growth, resazurin-integrated PADs can demonstrate chlorophenol inhibition effect on this Gram-positive strain in 80 min.

Toxicity Testing for Heavy Metals
The toxic effects of heavy metals on both E. faecalis and E. coli were detected by the resazurin-integrated PADs developed above at an OD 600nm 0.45. According to the color change on PADs (Figure 5), the obtained data (∆Hue) were fitted to Equation (1). The simulation results (k 1 and k 2 values) were summarized in Table 2. The R 2 of E. faecalis fitting results were more than 0.97 (>0.636, critical R 2 ) and the R 2 of E. coli fitting results were around 0.9 (>0.467, critical R 2 ). This suggested that the model (Equation   When using E. faecalis as a model, spiking three heavy metals (Cu 2+ , Zn 2+ , and Pb 2+ ) made the color change slower than the positive control group (Figure 5a). The ∆Hue values showed that the positive control group reached equilibrium at 30 min, while the heavy metal-spiked group did not reach it during the entire recording time (Figure 6a), showing heavy metal toxicity and suggesting that the presence of heavy metals inhibits bacterial activity and hence retards the resazurin reduction on PADs. Comparing the k 1 value in Table 2, there was no statistical difference in the reduction rate of resazurin on PADs among Cu 2+ , Zn 2+ , and Pb 2+ because the concentrations of these three heavy metals were all at IC 50 levels whose order was Cu 2+ < Zn 2+ < Pb 2+ . Hence, the toxicities of the three heavy metals were as reported [28]: Cu 2+ > Zn 2+ > Pb 2+ . However, the traditional method did not detect the toxicity of the three heavy metals to E. faecalis (Figure 6c).
With the same concentrations, Cu 2+ , Zn 2+ , and Pb 2+ were spiked into E. coli culture to evaluate the stress of heavy metals on such Gram-negative bacteria by growth-based inhibition method and resazurin-integrated PADs, respectively. The growth-based inhibition method cannot reveal the toxicity of those three heavy metals to E. coli (Figure 6d), similar to the finding for E. faecalis. However, the color change on resazurin-integrated PADs (Figures 5b and 6b) suggests that Cu 2+ , Zn 2+ , and Pb 2+ at IC 50 level show the same toxicity to E. coli. Comparing the k 1 value in Table 2, although there was no statistical difference among Cu 2+ , Zn 2+ , and Pb 2+ 's k 1 values on E. coli, their toxicity can be checked in 40 min (Figure 6b). heavy metal toxicity and suggesting that the presence of heavy metals inhibits bacterial activity and hence retards the resazurin reduction on PADs. Comparing the k1 value in Table 2, there was no statistical difference in the reduction rate of resazurin on PADs among Cu 2+ , Zn 2+ , and Pb 2+ because the concentrations of these three heavy metals were all at IC50 levels whose order was Cu 2+ < Zn 2+ < Pb 2+ . Hence, the toxicities of the three heavy metals were as reported [28]: Cu 2+ > Zn 2+ > Pb 2+ . However, the traditional method did not detect the toxicity of the three heavy metals to E. faecalis (Figure 6c).

Conclusions
The toxicity of several toxic substances to two types of bacteria, Gram-positive bacteria (E. faecalis) and Gram-negative bacteria (E. coli), was investigated by resazurin-integrated PADs. The color change on PADs and the kinetics of the resazurin reaction were used to assess the biotoxicity. Bacterial density is a key factor affecting the sensitivity of PADs' toxicity detection. Results show that OD 600nm 0.45 of E. faecalis and E. coli can differentiate the stress of PCP, 2,4-DCP, and 4-CP within 10 and 40 min, respectively. To further verify the applicability of this resazurin-integrated PADs, heavy metals, Cu 2+ , Zn 2+ , and Pb 2+ were used as toxicants for their biotoxicity detection. Similarly, according to the kinetics of resazurin reaction on PADs based on color change, the toxic effects of heavy metals on E. faecalis can be observed in only 10 min. All these results show that this resazurin-integrated PADs technology can detect the stress of toxic substances, including organic pollutants and heavy metals, in a gross way. The resazurin-based color response is targeted against reducing substances in living bacteria. The lack of selectivity is a limitation of resazurin-PAD. Integrating its sensitivity for toxicity differentiation, future work will involve modifying resazurin to make this resazurin-based assay selective for some important pollutants to study their synergistic or antagonistic or additive effects.
Supplementary Materials: The following supporting information can be downloaded at: https: //www.mdpi.com/article/10.3390/bios13050523/s1, Video S1: The PAD colorimetric response of E. faecalis to chlorophenol stress (pentachlorophenol, 2,4-dichlorophenol, and 4-chlorophenol) was sped up by a factor of 600 in the video. Video S2: The PAD colorimetric response of E. coli to chlorophenol stress (pentachlorophenol, 2,4-dichlorophenol, and 4-chlorophenol) was sped up by a factor of 600 in the video. Video S3: The PAD colorimetric response of E. faecalis to heavy metal stress (Cu 2+ , Zn 2+ , and Pb 2+ ) was sped up by a factor of 600 in the video. Video S4: The PAD colorimetric response of E. coli to heavy metal stress (Cu 2+ , Zn 2+ , and Pb 2+ ) was sped up by a factor of 600 in the video.