Yu-Ting Lin

Shang-Yu Yu

Hsiao-Wen Zan
email: hsiaowen@mail.nctu.edu.tw

Ping-Hung Yeh

Chia-Jung Lu

Hsin-Fei Meng

Chih-Wei Luo

Olivier Soppera

Photo-Assisted Recovery in Ammonia Sensor Based on Organic Vertical Diode

Keywords: Ammonia, fast recovery, light-assisted recovery, light emitting diode, organic gas sensor

In this article, a photo-assisted gas sensor was provided to solve the slow recovering issue of the organic gas sensor. The proposed organic gas sensor can detect ammonia in parts-per-billion regime in 30 seconds and can be multiple uses, but the long recovery time about 5 mins places difficulty to realize rapidly multiple-time sensing. Therefore, we used the photo-absorption ability in the organic semiconductor layer to generate the photocurrent and hence to compensate the current drop due to the ammonia absorption. The recovery time was significantly reduced to be only 1 min. The specific wavelength was also found to match the absorption spectrum in different organic sensing materials. As a comparison, the quartz crystal microbalance (QCM) was used to clarify the gas absorption and desorption mechanism. It is believed that this photo-assisted gas detection could be a general method to solve the slow recovery in organic-based gas sensors.

Graphical Abstract

Introduction

With the emerging development of the internet of things (IoT) technologies, the need for various kinds of solid-state sensors appears to be more and more important. Notably, the sensors for detecting the human body signals to reflect the health conditions are of high demand. In recent years, organic semiconducting devices are reported to exhibit a very high sensitivity to ammonia gas molecules [START_REF] Yang | Highly Sensitive Thin-Film Field-Effect Transistor Sensor for Ammonia with the DPP-Bithiophene Conjugated Polymer Entailing Thermally Cleavable tert-Butoxy Groups in the Side Chains[END_REF][START_REF] Lu | Tuning the Morphology of Isoindigo Donor-Acceptor Polymer Film for High Sensitivity Ammonia Sensor[END_REF][START_REF] Zhang | Solution-Processed Nanoporous Organic Semiconductor Thin Films: Toward Health and Environmental Monitoring of Volatile Markers[END_REF][START_REF] Lv | Gas Sensors Based on Polymer Field-Effect Transistors[END_REF]. Traditionally, ammonia detection is used in ambient air quality monitoring which requires the detection range in parts-per-million (ppm) regime. Recently, the ammonia detection in parts-per-billion (ppb) regime was reported to be useful in monitoring the spoilage of fish or several kinds of aquaculture products [START_REF] Chang | One-Minute Fish Freshness Evaluation by Testing the Volatile Amine Gas with an Ultrasensitive Porous-Electrode-Capped Organic Gas Sensor System[END_REF][START_REF] Heerthana | Biosensors: a potential tool for quality assurance and food safety pertaining to biogenic amines/volatile amines formation in aquaculture systems/products[END_REF], in controlling the clean room ambient, and in detecting ammonia in breath to reflect the health conditions of patients with chronic kidney diseases [START_REF] Chuang | Organic Gas Sensor with an Improved Lifetime for Detecting Breath Ammonia in Hemodialysis Patients[END_REF][START_REF] Hibbard | Point of Care Monitoring of Hemodialysis Patients with a Breath Ammonia Measurement Device Based on Printed Polyaniline Nanoparticle Sensors[END_REF][START_REF] Ishida | The breath ammonia measurement of the hemodialysis with a QCM-NH3 sensor[END_REF] or with Helicobacter pylori infection [START_REF] Kearney | Breath Ammonia Measurement in Helicobacter pylori Infection[END_REF]. Organic semiconductor devices exhibit the advantages of low production cost and the ability to detect ammonia in ppb-regime. Thus, they are promising to be used to develop abovementioned applications.

However, to push into the real applications, the requirements on sensors are more than high sensitivity and low production cost. Key factors such as selectivity, a long lifetime in the air, and multiply-used ability are all critical. In prior reports, organic-based ammonia sensors can be roughly divided into two kinds of devices. The first kind uses a transistor structure [START_REF] Yu | Morphology-Driven High-Performance Polymer Transistor-based Ammonia Gas Sensor[END_REF][START_REF] Peng | Solution-Processed Monolayer Organic Crystals for High-Performance Field-Effect Transistors and Ultrasensitive Gas Sensors[END_REF][START_REF] Ge | Bar-Coated Ultrathin Semiconductors from Polymer Blend for One-Step Organic Field-Effect Transistors[END_REF]. The second kind uses the vertical diode structure which was proposed by our group [START_REF] Chuang | Organic Gas Sensor with an Improved Lifetime for Detecting Breath Ammonia in Hemodialysis Patients[END_REF][START_REF] Chuang | Gas permeable silver nanowire electrode for realizing vertical type sensitive gas sensor[END_REF][START_REF] Chuang | Modulated gas sensor based on vertical organic diode with blended channel for ppb-regime detection[END_REF]. For both transistor structure and vertical diode structure, the sensors have ppb-regime sensitivity to ammonia. The selectivity among ethanol, acetone, nitric oxide, carbon dioxide is also verified to be good enough in prior works [START_REF] Dai | Highly Sensitive Ammonia Sensor with Organic Vertical Nanojunctions for Noninvasive Detection of Hepatic Injury[END_REF][START_REF] Li | High Performance Field-Effect Ammonia Sensors Based on a Structured Ultrathin Organic Semiconductor Film[END_REF][START_REF] Wang | Solution-Processed Microporous Semiconductor Films for High-Performance Chemical Sensors[END_REF]. The long-enough lifetime in air (64 days) was reported by our prior work [START_REF] Chuang | Organic Gas Sensor with an Improved Lifetime for Detecting Breath Ammonia in Hemodialysis Patients[END_REF]. The multiple-used stability in air was also verified by many groups [START_REF] Kumar | Electrical and Ammonia Gas Sensing Properties of PQT-12/CdSe Quantum Dots Composite-Based Organic Thin Film Transistors[END_REF][START_REF] Nketia-Yawson | Highly Sensitive Flexible NH3 Sensors Based on Printed Organic Transistors with Fluorinated Conjugated Polymers[END_REF][START_REF] Han | Poly(3-hexylthiophene)/polystyrene (P3HT/PS) blends based organic field-effect transistor ammonia gas sensor[END_REF][START_REF] Khim | Precisely Controlled Ultrathin Conjugated Polymer Films for Large Area Transparent Transistors and Highly Sensitive Chemical Sensors[END_REF]. However, all the reported works suffer from a slow recovery time (i.e., 3-10 mins), compared to the fast detecting time (i.e., 5-60 s). The slow recovery time places a limitation on the applications. For example, for in-line meat freshness detection or for breath ammonia detection in the hospital, the 5 mins recovery causes user impatient and a long queue of waited samples.

Here in this work, we fabricated a sensitive ammonia sensor by using an air-stable donor-acceptor [3,4-b]thiophenediyl]] (PBDTTT-C-T). Then, we proposed a lightassisted method to greatly reduce the recovery time from 300 s to 60 s. The wavelength dependency on the photo-assisted recovery time was observed. Also, the multiple sensing stability is confirmed to be good enough with the light-assisted recovery. The mechanism is also investigated by comparing the light-induced current variation in the organic vertical diode and the light-induced desorption in quartz crystal microbalance (QCM) devices. We concluded that the light-assisted recovery is mostly achieved by compensating the effect of ammonia-induced carrier reduction with the light-generated photocarriers.

(D-A) type polymer, Poly[[4,8-bis[5-(2-ethylhexyl)-2-thienyl]benzo[1,2-b:4,5-b']dithiophene-2,6- diyl][2-(2-ethyl-1-oxohexyl)thieno

Experimental section

Sensor fabrication

Fig. 1(a) shows the fabrication process of the ammonia sensor with vertical channels on the sidewall of cylindrical nanopores [START_REF] Chuang | Organic Gas Sensor with an Improved Lifetime for Detecting Breath Ammonia in Hemodialysis Patients[END_REF]. The cylindrical nanopores were fabricated via the colloidal lithography method. Firstly, a glass substrate with patterned indium tin oxide (ITO) (sheet resistance as 6 Ohm/square) was treated with oxygen plasma (100 W 600 s) to form a hydrophilic surface. A cross-linkable Poly(4-vinylphenol) (PVP) layer (thickness ~ 300 nm) was then spin-coated on the ITO substrate and annealed at 200 °C for 1 hr. to serve as the insulating layer. To modify the PVP surface to favor the subsequent adhesion of negatively charged polystyrene (PS) nano-spheres (Fluka, 200 nm diameter), a thin layer of Poly(3-hexylthiophene-2,5-diyl) (P3HT) was spin-coated onto PVP and annealed at 200 °C for 10 mins. Then, the substrate was immersed into PS solution (10 wt% in ethanol) for 90 s and dipped into boiling isopropanol (IPA) for 10 s to remove excess PS spheres. After quickly drying out the substrate with nitrogen flow, the monolayer PS nano-spheres was formed to serve as a shadow mask for Al electrode deposition. After evaporating a 60-nm-thick Al layer (evaporation rate as 0.15 nm/s), the PS nano-spheres were then peeled off with 3M Scotch Tape to obtain porous Al top electrode. The porous top electrode was further served as another shadow mask for subsequent oxygen plasma etching. During the plasma etching process, the PVP in the area not covered by the top electrode was removed, thus forming the cylindrical nanopore structure. Finally, two different types of active layer were deposited onto the structure and annealed at different temperatures, enabling the conduction of vertical current. For the proposed air-stable device, PBDTTT-C-T (0.9 wt% in chlorobenzene) was blade coated onto the nanopore substrate with the blade speed of 200 mm/s. The substrate was, then, annealed at 80 °C for 10 mins. The resulting thickness of PBDTTT-C-T is around 40-50 nm. For the control sample, P3HT (1.5 wt% in chlorobenzene) was spin-coated on to the substrate and was annealed at 200 °C for 10 mins. The thickness of P3HT is around 35-45 nm.

Sensing system with a light irradiation control

The gas sensing system is as depicted in Fig. S1 in supporting information. The system comprised a transparent sensing chamber, a desiccation cylinder (sodium hydroxide (NaOH)) to provide a steady relative humidity (RH) around 10% and eliminate the interference from ambiance RH variation, an electric source measurement unit (Keysight U2722A USB modular) to apply operational voltage on sensor and read out electric signal, a rotameter to control the flow at 500 cc/min, a pump to provide a constant air flow, and a humidity measurement unit to confirm the RH value during experiment. To study the effect of light irradiation and to prevent the light interference from the ambiance, the transparent sensing chamber with the mounted sensor was placed inside an opaque box, as shown in Fig. 1(b). Different light-emitting diodes (LEDs) were utilized to irradiate light onto the sensor, sequentially. The wavelength and the irradiance of various LED light sources are 465 nm (630 µW/cm 2 ), 620 nm (210 µW/cm 2 ), and 730 nm (12 µW/cm 2 ).

QCM measurement

To investigate the molecular absorption/desorption during light irradiation, we formed the identical sensing layer, PBDTTT-C-T with 40-50 nm thickness, onto the QCM chip (purchased from Seiko) by using the dip-coating process. Then, the frequency of QCM chip was measured by using QCM922A (Seiko) upon ammonia injection/removal when the QCM chip was placed in dark or under light irradiation.

Results and discussion

The scanning electron microscope (SEM) image of the nanoporous substrate was shown in Fig. 2(a). This nanoporous structure (or 3D structure) increases the detection area, and the vertical channel greatly reduces the channel length to be 300 nm. Hence, the sensor exhibits a high sensitivity to low concentration ammonia (i.e., 100 ppb) and delivers high output current as a few microamperes at 5 V. It is noted that organic semiconductor material usually exhibits low mobility, the hole mobility for PTBTTT-C-T was 1.3Í 10 -2 cm 2 V -1 s -1 in the prior report [START_REF] Luo | Remarkable enhancement of charge carrier mobility of conjugated polymer field-effect transistors upon incorporating an ionic additive[END_REF]. The current-voltage characteristic of the PBDTTT-C-T sensor was shown in Fig. 2(b). It could be observed that at the turn-on voltage around 4 V, the turn-on curve shows a Schottky conduction behavior, which is due to the presence of injection barrier from ITO (work function as 5 eV after oxygen plasma treatment) to PBDTTT-C-T (highest occupied molecular orbital, HOMO, as 5.2 eV). The real-time sensing phenomenon was shown in Fig. 2(c) by plotting sensing responses as a function of time. The orange background region indicates the periods when the ammonia with different concentrations (100 ppb to 1 ppm) was injected into the sensing chamber. The carrier gas is dry air with relative humidity around 10%, and the pump rate is fixed as 500 cc/min. The sensing response is calculated by the current variation value divided by the initial current value right before gas injection. The sensing period was set as 30 s. It could be seen that with only 30 s ammonia injection, the sensor exhibits substantial responses to different concentration of ammonia. Specifically, the sensing response to 100 ppb ammonia reaches 14.9 %. Even though the sensing requires only 30 s, in Fig. 2(c), we noticed that the current recovery is rather slow. After 100 ppb ammonia detection, it takes 183 s of recovery time for the current returns to its original current level, denoting the zero response value. With increasing ammonia concentration, the recovery time is significantly increased from 183 s to 490 s for 1000 ppb ammonia detection. However, the sufficient recovery time is of paramount requirement for multiple sensing performances in the organic sensor. If the multiple testing is done with insufficient recovery time, the response becomes smaller and smaller along with the testing times. As shown in Fig. 2(d), for the repeated 300 ppb ammonia testing for five times, the normalized responses stayed almost unchanged when the recovery time is 300 s while the normalized response gradually decreases when the recovery time is 180 s (insufficient recovery). If the ammonia concentration increases to be 2 ppm and the recovery time is only 180 s (insufficient recovery), then the normalized response significantly drops along with test times. Hence, sufficient recovery is needed to keep the sensor stability. However, such a long recovery time then places a limit on the rapidly multiple-time testing applications.

To reduce the recovery time, we may think of enhancing the gas desorption by increasing the pumping flow rate or by heating up the samples. However, the two approaches also take time to reach a stable condition. So, they are not suitable if the targeting recovery time is within 1 minute. In this study, we propose a light irradiating method to reduce the recovery time (photo-assisted recovery). The set-up is shown in Fig. 1(b). To study the influence of light irradiating on recovery phenomenon and its dependency on light wavelength, the light recovery performance of two different sensors, PBDTTT-C-T sensor and P3HT sensor, was investigated. The P3HT sensor was chosen as a control sample to study the wavelength dependency on the photo-assisted recovery due to its absorption wavelength different from that of PBDTTT-C-T. The absorption spectrums of these two materials were shown in Fig. 3(a). The P3HT exhibited an absorption peak around 515 nm, whereas those of PDBTTT-C-T were at 645 nm and 704 nm. The response as a function of time for PBDTTT-C-T sensor and P3HT sensor were plotted in Figs. 3(b) and 3(c), respectively. The orange regions indicate the 30 s injection of 300 ppb ammonia. After a 30 s sensing time, the LED is turned on to irradiate the sample. Total 3 LEDs with the wavelength of 730 nm, 620 nm, and 465 nm were used in this study. The irradiance of each LED was 12 µW/cm 2 , 210 µW/cm 2 , and 630 µW/cm 2 , respectively. The response curves with different LEDs irradiating and without LED irradiating (i.e., in dark) are compared. In Fig. 3(b), the real-time response curve of PBDTTT-C-T sensor, we can observe that compared to the recovery curve obtained in dark, the recovery process was faster when the sensor was irradiated with LED light, and the recovery time of the sensor irradiated with different LED light source were varied. Moreover, the same phenomenon can be observed in P3HT sensor as shown in Fig. 3(c). However, for P3HT sensor, the recovery curve obtained by 730 nm LED irradiation showed no significant different to that of in dark, indicating that 730 nm light has no significant effect on the recovery process. The results above revealed that the effect of photo-assisted recovery is linked to two factors, the absorbance of the sensing material and the irradiance of the LED light source. To understand the relationship of these two factors to the photo-assisted recovery process, we, therefore, extracted the absorbance intensity of both PBDTTT-C-T and P3HT materials at the center wavelength of 3 LEDs (456nm, 620 nm, and 730 nm) and the recovery time of both sensors under the irradiation of 3 LEDs, and plotted as a function of LED light source as shown in Fig. 3 (d). It can be observed that with the LED light source of 730 nm, the PBDTTT-C-T exhibited a greater absorption than that of P3HT which is nearly negligible. Hence, with the relatively low irradiance of 730 nm LED irradiation, the PBDTTT-C-T sensor showed a huge reduction of recovery time, whereas no significant effect was found in the P3HT sensor. At the wavelength of 620 nm, an alike absorbance can be seen in both material, resulted in a similar effect of the reduction of recovery time. Nevertheless, with the 465 nm LED irradiation, the P3HT sensor displayed a huge reduction of recovery time compared to that of PBDTTT-C-T sensor due to the great absorption property of P3HT material to 465 nm light source. Moreover, thanks to the strong irradiance of 465 nm light source, the recovery time of the PBDTTT-C-T and P3HT sensors can be reduced to 40 s and 2 s, respectively. Finally, since our targeting recovery time is within 1 minute and the maximum irradiance of LEDs were limited by the output performance of LEDs, we choose 465 nm LED as the light source in the following experiments. Also, even though P3HT has a smaller recovery time, P3HT sensors has only 2-days lifetime in air (Fig. S2 in the supporting information). On the contrary, PBDTTT-C-T sensor exhibits a more than 15-days lifetime. Hence, in the following section, we choose PBDTTT-C-T as the proposed gas sensor and use 465 nm LED to study the mechanism of light/sensor interaction.

As previously discussed, sensor current can be quickly recovered with the 465 nm LED irradiating. However, to be ready for the next testing, LED needs to be turned off to keep the sensor in dark again. It is noted that, if the sensor is always operated under LED irradiation, the sensing response will degrade due to the constant elevation of the background carrier density under irradiation. Hence, after turning off the LED, an additional time is needed to stabilize the sensor current because the light current generated by LED is removed from the sensor. As a result, for every gas sensing test, the operating sequence was designed as the following three steps (in Fig. 4(a)). (I) Injecting ammonia for 30 s. (sensing period). (I) Irradiating LED for 40 s. (recovery period). (III) Turning off LED and stabilizing sensor current for 20 s. (stabilizing period). It is noted that the current drops in stabilizing period because the photo-generated carriers are reduced after turning off the LED. The sufficient duration for recovery period and for stabilizing period can be confirmed by plotting the current variation as a function of time in Fig. 4(b). When turning on the LED, the current increases suddenly, hence a positive current variation is obtained. Then, during the 30 s of the irradiation, the current gradually increases to reach a saturated value and the current variation reduces to be almost zero. Therefore, it is enough to set the 40 s light irradiation as the "recovery period" to reach a full recovery. When turning off the LED, the current drops and the current variation is negative. After 20 s, the current variation becomes almost zero. As a result, we use 20 s to define the stabilizing period.

With the proposed operation sequence, we then verify the feasibility by performing multiple testing. We firstly examined if the sensing response can be kept during 5-times 300 ppb ammonia sensing in Fig. 4(c). The sensing periods (30 s ammonia injection), the recovery periods (40 s LED on), and the stabilizing periods (20 s) are represented by orange, blue, and white regions, respectively.

With the fast photo-assisted recovery, the multiple testing can be done within 90 s. The responses for each time of sensing were plotted in the lower part of the figure. A good enough sensing stability can be observed. We further verify the multiple-time sensing performance by injecting ammonia with various concentrations for 20 times. As shown in Fig. 4(d), the ammonia concentration as 100/300/500/1000/2000 ppb is injected into the sensing chamber in a random order. The final responses are plotted as a function of concentration in Fig. 4(e). For every different concentration, at least 3-times testing are done. The small standard deviations in Fig. 4(e) verify that the proposed photoassisted recovery method is suitable to realize a fast and stable multiple-times ammonia sensing. It is noted that the response in continuously multiple testing is smaller than the single time testing. For example, when detecting 300 ppb ammonia for one time, the response is around 23% in Fig. 2(c). In photo-assisted multiple testing mode, the response reduces to be about 13% as in Fig. 4(a). The phenomena make us suggest that the photo-assisted fast recovery is not due to the enhancement of the ammonia desorption, but a superposition of the current increase under light irradiation onto the current drop under gas sensing. Hence, with the remaining ammonia inside the active layer, the response becomes smaller in the multiple testing mode. However, as shown in Fig. 4(d), the response reaches a new stabilized condition and successfully delivers a stable calibration curve in Fig. 4(e). Then, we like to investigate the underlying mechanism of the photo-assisted recovery. The primary interest is to clarify if the there is any enhanced gas desorption under light irradiation. In volatile organic compounds (VOCs) sensors based on oxide material such as ZnO, UV light is usually used to enhance the density of the weak-bounded oxygen and then to improve the reaction between VOC species and the absorbed oxygen [START_REF] Jaisutti | Low-Temperature Photochemically Activated Amorphous Indium-Gallium-Zinc Oxide for Highly Stable Room-Temperature Gas Sensors[END_REF]. Here, in ammonia sensor based on the organic semiconductor material, it is believed that the current reduction in the p-type organic semiconductor is because that the electron lone pair in ammonia molecules serve as traps for holes to de-dope the semiconductor and hence reduce the current [START_REF] Chuang | Organic Gas Sensor with an Improved Lifetime for Detecting Breath Ammonia in Hemodialysis Patients[END_REF][START_REF] Zhou | An ammonia detecting mechanism for organic transistors as revealed by their recovery processes[END_REF][START_REF] Tiwari | Poly-3hexylthiophene based organic field-effect transistor: Detection of low concentration of ammonia[END_REF]. Under light irradiation, additional photogenerated carriers increase the current of the device. Hence, it is possible that the photo-assisted recovery is simply the superposition of the gas sensing current plus the light detecting current. To verify the proposed mechanism, we designed two sets of experiments. In the first experiment, we measure the pure gas sensing response and the pure light irradiating response as shown in Fig. 5. The response is the current variation ratio. The black curve represents the response under 30 s detection (t = 0 s ~ t = 30 s) of 300 ppb ammonia and then recovered in dark. The blue curve represents the response of the sensor without contacting any ammonia and was irradiated by light at t = 30 s. When adding the black and the blue lines together, the result is the green line. Finally, the response of the sample exposed to ammonia and then irradiated by LED is also plotted in Fig. 5 as the red line. A good overlap between the green and the red lines is obtained, indicating that the photo-assisted recovery is simply using the photo-generated carrier to overcome the current drop during the ammonia sensing. There may be no enhanced gas desorption during light irradiation. To further confirm this phenomenon, we did the second set of experiment. We utilized the quartz crystal microbalance (QCM) to help examine if there is any enhanced ammonia desorption from PBDTTT-C-T during LED irradiation. The result is shown in Fig. 6(a), in which the frequency shift of the PBDTTT-C-T coated QCM chip is plotted as a function of time. The orange region indicates the 30 s injection of 300 ppb ammonia, then the recovery is observed in dark and under LED irradiation. In the recovery period, in the initial 30 s, LED irradiation indeed enhance the desorption of ammonia, so the frequency shift exhibit a fast recovery in the beginning 30 s. However, after t = 60 s, the QCM sample has a prolonged recovery. The full recovery is achieved after 273 s for the sample under LED irradiation. When we plot the PBDTTT-C-T sensor response as a function of time in Fig. 6(b), the orange region also represents the 30 s injection of 300 ppb ammonia. After removing the ammonia, the response quickly recovers to be zero within 30 s. We hence conclude that, under LED irradiation, there is a little bit light enhanced desorption. However, the main reason to achieve a fast recovery is because the light generated current compensates the current reduction due to ammonia. The proposed mechanism is illustrated in Fig. 6(c). When PBDTTT-C-T sensor is exposed to ammonia, the absorbed ammonia molecules serve as hole trapping centers to reduce the hole current. Then, after turn on LED light, the photo-generated current provides additional electron-hole pairs to increase the current level. The ammonia molecules still undergo a slow desorption process. The successful multiple testing in Fig. 4 verifies that, even with remaining ammonia molecules, the PBDTTT-C-T sensor can repeatedly response to the absorbed ammonia in the multiple tests. It is believed that the multiple testing is successful because the ammonia concentration in this study is low. The reacting-site density in PBDTTT-C-T is much higher than the absorbed ammonia density. Hence, the sensor current can keep detecting newly absorbed ammonia molecules even when there are remaining ammonia molecules inside the sensing film.

Conclusions

In this work, we provided a photo-assisted gas detection method to improve the recovery time and solve the dilemma. The PBDTTT-C-T organic semiconductor was chosen as the sensing material to provide good sensitivity to ammonia in parts-per-billion (ppb) regime and also to exhibit a good lifetime (> 14 days) in air. When the sensing of 300 ppb ammonia takes only 30 s to deliver an apparent current drop, the recovery requires 300 s to let the current returns to its original value. When ammonia concentration increases to be 1 ppm, the recovery time is as long as 490 s. Using blue light irradiation during the recovery period can greatly reduce the recovery time to be less than 60 s. It was confirmed that such a photo-assisted recovery is not mainly due to the improved gas desorption under light irradiation, but due to the current compensation effect. The current drop after ammonia detection is compensated by the current increase under light irradiation. As a result, the fast multiple-time sensing gradually increases the amount of remaining ammonia residue inside the sensing film. Nevertheless, because of the low targeting detection range of 100 ppb to 2000 ppb, a certain amount of reacting sites in PBDTTT-C-T can still react with the following ammonia molecules after the first sensing process.

A new kinetic balance of gas desorption and absorption can be reached, enabling a reliable multiple testing performance. The proposed photo-assisted measurement takes only 90 s to complete a detecting cycle. We verified that, within one hour, 20-times testing to ammonia concentration ranged from 100 ppb to 2000 ppb delivers a reliable calibration curve. Therefore, we conclude that the photo-assisted gas sensing is a practical method to solve the long recovery time in organic-based gas sensors. The proposed sensitive and stable ammonia sensor, together with the fast-operated photo-assisted system, is promising for developing real applications in industrial gas sampling or on-line fish freshness testing.

Fig. 1 .

 1 Fig. 1. Schematic diagram of (a) the fabrication process of cylindrical nanopores structure for organic ammonia sensor and (b) the design of light-assisted gas sensing system.

Fig. 2 .

 2 Fig. 2. (a) The scanning electron microscope (SEM) of the cylindrical nanopores structure. (b) The I-V characteristic of PBDTTT-C-T sensor. (c) The real-time responses of PBDTTT-C-T sensor to ammonia concentration of 100 ppb, 300 ppb, 500 ppb, and 1000 ppb, respectively. The orange area indicates 30 s of the ammonia gas injection. The period for the response to recover to zero value was defined as the recovery time and is indicated at the respective sensing curve. (d) The normalized response of 5 times repeated sensing to 300 ppb, and 2000 ppb ammonia concentration, respectively. The black and red curve indicated 300 s and 180 s recovery time between each sensing process, respectively.

Fig. 3 .

 3 Fig. 3. (a) The UV-visible absorption spectrum of P3HT and PBDTTT-C-T organic polymer. The realtime measurement of (b) PBDTTT-C-T sensor and (c) P3HT sensor responses to 300 ppb ammonia concentration in dark or under different light source irradiation. The wavelength of 3 LED light sources are 465, 620, and 730 nm, respectively. (d) The dependency of recovery time and the corresponding absorbance of P3HT and PBDTTT-C-T sensor to the various wavelength light sources. The red and blue dot-lines indicate the recovery times without light irradiation for P3HT and PBDTTT-C-T sensors, respectively.

Fig. 4 .

 4 Fig. 4. (a) Real-time current measurement of PBDTTT-C-T sensor under three steps of the proposed light-assisted operation sequence: (I) Injection of ammonia for 30 s. (sensing period, orange region). (II) LED irradiation for 40 s. (recovery period, blue region). (III) Dark state for sensor stabilizing for 20 s. (stabilizing period, white region). (b) Current variation plotted as a function of time (c) Real-time current measurement and corresponding ammonia sensing response of PBDTTT-C-T sensor to 300

Fig. 5 .

 5 Fig. 5. Real-time responses of PBDTTT-C-T sensor in different conditions: The blue curve represents the condition of only light irradiation without gas exposure. The red curve represents the condition of the sensor firstly exposed to ammonia then recovered under light irradiation. The black curve represents the condition of only gas exposure without light irradiation. The green curve shows the superposition of blue and black curves.

Fig. 6 .

 6 Fig. 6. (a) Real-time quartz crystal microbalance (QCM) measurement of PBDTTT-C-T thin film exposed to 300 ppb ammonia then recovered with and without light irradiation. (b) Real-time response of PBDTTT-C-T sensor exposed to 300 ppb ammonia then recovered with and without light irradiation. (c) The schematic drawing of the ammonia sensing mechanism in PBDTTT-C-T sensor and the mechanism of the proposed light-assisted recovery.

Fig. S1 .

 S1 Fig. S1. The schematic drawing of the designed light-assisted gas sensing system. The blue arrows indicated the gas flow direction.

Fig. S2 .

 S2 Fig. S2. The decayed responses of PBDTTT-C-T and P3HT sensors in different days. The decayed response is defined as the sensing response divided by its initial response value.

Acknowledgment

The authors would like to acknowledge the support by Ministry of Science and Technology, Taiwan (Project 106-2112-M-032-006 and 107-2112-M-032-006)

Appendix A. Supporting information

Supplementary data associated with this article can be found in the online version

Supporting information


domain: spi qfin

text:
Call for papers -Special Issue

"Do-It-Together" and innovation, towards the Factories of the Future (FoF) Guest Editor(s): Laurent Dupont1 , Fedoua Kasmi 1 , Joshua M. Pearce2 , Roland J. Ortt3 Faced with the environmental and socio-economic limitations of the current production model, that has persisted for several years, the accelerated development of information and communication technologies has made it possible to explore new innovative fields in the productive sectors. New reflections are emerging on the transition towards a more sustainable and innovative production models. In this context, the emerging "Design Global, Manufacture Local" model (DGML), aims at transforming the global manufacturing industry so that the vast majority of products can be manufactured locally by globally exchanging the information flows on how to manufacture the product (information, knowledge, design, codes, models, drawings, etc.) over the physical flows [START_REF] Kostakis | Design global, manufacture local: Exploring the contours of an emerging productive model[END_REF][START_REF] Kostakis | The convergence of digital commons with local manufacturing from a degrowth perspective: Two illustrative cases[END_REF]Waldman Brown, 2016). This model is based on the principles of commons-based peer production [START_REF] Bauwens | The Political Economy of Peer Production[END_REF][START_REF] Kostakis | Design global, manufacture local: Exploring the contours of an emerging productive model[END_REF] in which resources are shared with equal interest for all the involved stakeholder [START_REF] Ostrom | Governing the Commons: The Evolution of Institutions for Collective Action[END_REF]. It represents a form of democratization of the industrialization through processes in which the design is developed as a global common, while the manufacture of products takes place locally, considering the specificities of local ecosystems.

The mode of commons-based peer production, particularly digital commons, has mainly developed within the so-called Makers' movement, also known as the Do-It-Yourself (DIY) movement. The emergence and multiplication of spaces and networks of makers, hackerspaces, micro-factories, fab labs or other spaces equipped with digital manufacturing tools and technologies (3D printers, sensors...) has favoured the development of a more agile, democratized and distributed production [START_REF] Kohtala | Anticipated environmental sustainability of personal fabrication[END_REF][START_REF] Pearce | Open-Source Lab How to Build Your Own Hardware and Reduce Research Costs[END_REF][START_REF] Fox | Paradigm shift: Do-it-yourself (DIY) invention and production of physical goods for use or sale[END_REF][START_REF] Dupont | Agile innovation: Creating value in uncertain environments[END_REF]. Such environments are conducive to distributed collective creativity, which plays an important role in the emergence of new forms of innovation and entrepreneurial activities [START_REF] Capdevila | Les différentes approches entrepreneuriales dans les espaces ouverts d'innovation[END_REF]2019;Boutillier et al., 2018). Based on the customization, integration and involvement of users in the production processes and local production in small series, the DIY practices represent a source of the development of "prosumption (local production with local materials by local people), innovation, and entrepreneurship by local populations in regions without industrial manufacturing infrastructure" [START_REF] Fox | Third Wave Do-It-Yourself (DIY): Potential for prosumption, innovation, and entrepreneurship by local populations in regions without industrial manufacturing infrastructure[END_REF]. The confluence of ideas and technologies and the interconnection between digital and physical environments offer the potential for a transition to a new form of hybrid production that combines the scale and efficiency of high-volume manufacturing with the benefits that small local producers (SMEs and SMIs) bring to local economies [START_REF] Fox | Third Wave Do-It-Yourself (DIY): Potential for prosumption, innovation, and entrepreneurship by local populations in regions without industrial manufacturing infrastructure[END_REF]Waldman Brown, 2016). Nevertheless, supporting this hybrid production approach and disseminating the do-it-yourself principles among local producers requires the development of new production modes and strategies in a context where processes "are less open, less distributed and less minimal than the new Do-It-Yourself processes" [START_REF] Fox | Paradigm shift: Do-it-yourself (DIY) invention and production of physical goods for use or sale[END_REF]. As a result, many actors, especially small producers, miss the opportunities of development and innovation offered by the DIY.

The new "Do-It-Together" (DIT) approach attempts to address these limitations. It is a participatory design and collaborative production strategy that allows "global design and local manufacturing" involving "prosumers" (consumers/producers) [START_REF] Toffler | The third wave[END_REF] in the manufacturing process. It has recently been developed in the context of social manufacturing, which is a more open and democratic approach to traditional manufacturing, involving different levels of user participation in the production process (Shang et al. 2013;[START_REF] Hirscher | Social manufacturing in the fashion sector: New value creation through alternative design strategies[END_REF]. The social manufacturing approach aims to "seamlessly link the social manufacturing network consisting of the Internet, the Internet of Things, and the 3D printer, thus enabling social people to participate fully in the entire manufacturing process through outsourcing, facilitating personalized, real-time, and socialized modes of production and consumption" [START_REF] Mohajeri | The impact of social manufacturing on the value chain model in the apparel industry[END_REF]. It integrates consumers in all the processes of customized product development, such as ideation, design and production, engaging them more actively in local production in a commons-based peer production context, inspired by the agile and distributed functioning of the DIY [START_REF] Hirscher | Social manufacturing in the fashion sector: New value creation through alternative design strategies[END_REF].

The first studies on the collaborative creativity practices of the Do-It-Together have examined its impact on the creation of value in the fashion industry. Social, economic, environmental, knowledge, emotional and experiential values associated with the DIT were identified, generating positive externalities for all the involved stakeholders (customers, professionals and local producers) [START_REF] Hirscher | Social manufacturing in the fashion sector: New value creation through alternative design strategies[END_REF]. The DIT strategies are indeed adapted to small-scale production on local sites offering significant potential for new business opportunities and new innovative activities especially for SMEs that face many challenges to engage open innovation processes. The potential for open creativity generated by the DIT can provide competitive advantages for companies while limiting the costs and risks associated with the development of innovative products [START_REF] Cullmann | Participative creativity serving product design in SMEs: a case study[END_REF].

Building on social manufacturing paradigms such as cyber-physical-social space that "involves human intelligences and social organizations (e.g. communities) to enable social interactions and organic connections between prosumers and socialized resources (e.g. machine tools, design software, measurement equipment and sensors) to co-create individualized products and services" [START_REF] Jiang | Social manufacturing: A survey of the state-of-the-art and future challenges[END_REF] the DIT strategies would enable the development of connected open innovation networks coordinated by multi-sided digital platforms. These platforms support co-creative communities in the form of distributed value networks in a collaborative economy context (Gandia, Guy, 2020). The DIT networks link consumers, makers, micro-factories and small local producers, making their production capacities available to the local ecosystem and forming regional poles of industrial innovation that could disrupt the functioning of the current production systems.

The emergence of the Do-It-Together approach could be integrated within the EU's Factories of the Future (FoF) strategy that aims at a transition of the European manufacturing industry towards a more flexible, digital and demand-oriented industry. It is in this context that the INEDIT 4 H2020 research project seeks to set the conceptual and experimental basis for the understanding of the DIT concept and to explore its potential for the transition of the industrial systems towards a disruptive change inducing radical innovations [START_REF] Dedehayir | Reconfiguring the innovation ecosystem: An explorative study of disruptive change[END_REF]. To this purpose, this special issue calls for interdisciplinary research to deepen the analysis of this novel approach. The different disciplines in economics, management and engineering of innovation could be mobilized in order to:

• Enrich the conceptualization of the DIT approach and study its potential for the development of different forms of innovation. Submit abstracts or questions to: l.dupont@univ-lorraine.fr ; fedoua.kasmi@univ-lorraine.fr

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  Study the impact of the innovation processes generated by the DIT on organizations and territories. • Examine the different types of co-creation values generated by the DIT collaborative approach. • Analyze the potential for reorientation of design and manufacturing practices. • Study the role of the implementation of the DIT processes in the emergence of new business opportunities and the creation of innovative entrepreneurial activities • Analyze the prospects for environmental sustainability. The topics addressed in this issue could include among other the following reflections: • The role of the implementation of the Do-It-Together processes in the emergence of open innovation ecosystems and the creation of actors' networks based on the exchange of value and new forms of collaboration. • The new values created through the integration of the consumer/user or open community in the co-creation, co-design and co-production phases and the transition of the consumer/user from a value user to a value creator. • The role of the new technologies developed around the involvement of users in co-creation processes such as immersive technologies and artificial intelligence and their ability to accelerate both creativity and innovative conception in companies. • The impact of the introduction of disruptive technologies, machines and open production methods (additive manufacturing methods, open-hardware approaches...) usually used by the Makers and Fablabs communities on the innovation capacities of companies and their role in the optimization of production and the increase of economic, technological, organizational and environmental performances. • The role of new digital technologies in the development of open innovation networks and in the integration of structural changes on the process of co-creating, co-designing and coproducing. • The emergence of new business models and the necessary changes for their implementation within the Do-It-Together processes. Timetable for submission and acceptance of papers: Deadline for complete manuscripts through online paper submission: 01 November 2020 http://www.editorialmanager.com/innovations/default.aspx Guideline for authors: http://www.cairn.info/docs/Instructions_for_authorsGB110816.pdf -Final notification for acceptance: 30 November 2021

ERPI Laboratory (Research Team on innovative Processes), Université de Lorraine, France

Department of Materials Science and Engineering and Department of Electrical & Computer Engineering, Michigan Technological University

Department of Values, Technology & Innovation (VTI), Section Economics of Technology and Innovation (ETI), Delft University of Technology

open INnovation Ecosystems for Do It Together process, European Union's H2020 research program -Agreement N 869952, http://www.inedit-project.eu/