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30 protocols using al204

1

Degradation Evaluation of Scaffolds

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To evaluation the degradable properties of the scaffolds, the weight change of the samples before and after soaking into phosphate buffer saline (PBS) for up to 84 days was monitored by the electronic analytical balance (AL204, Mettler Toledo, Switzerland), and the weight change ratio was calculated according to the following equation:18 (link) weight change (%) = (WnW0)/W0, where W0 represents the samples weight before soaking and Wn represents samples weight after soaking for different times. In addition, the change of pH value in solution for the scaffolds during the immersion period was also measured by a pH meter (FE20K, Mettler Toledo, Switzerland) at designated points of time.
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2

Biomass and Nutrient Determination in Seedlings

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The sampled seedlings were washed with water and dried in the shade, fixed at 105 ℃ for 15 min, and dried at 75 °C to achieve a stable weight. The samples’ dry biomass was measured with 0.001 g accuracy by electronic scales (AL204, Mettler-Toledo, Melbourne, Australia) [48 (link)]. Seedlings were prepared for analytical sampling by grinding with a plant crusher and then processing the material through a 0.5 mm plastic sieve. Total N, P, and K of seedlings were dissolved with the H2SO4-HClO4 method, soil total P and K with the NaOH solution-melting method, and soil total N with concentrated sulfuric acid and mixed catalyst (K2SO4: CuSO4 = 10:1). N, P, and K contents were determined by the Kjeldahl method (ATN-300, Hongji, Shanghai, China) [53 (link)], the molybdenum-antimony colorimetric method (UV-2600A, Unicom, Shanghai, China) [54 (link)], and the atomic absorption spectrophotometer method (AA7002, Dongxi, Beijing, China) [55 (link)], respectively. Each indicator was repeated three times. Plant N (P, K) accumulations (mg·plant−1) were obtained by multiplying dry biomass (g·plant−1) by N (P, K) content (g·Kg−1). Plant biomass and the N, P, and K accumulation of each fertilizer combination are listed in Table 7.
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3

Growth and Feeding Dynamics of Shrimp

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Before the experiment, S. intermedius individuals in each treatment were dried with a paper towel and weighed on a digital balance (0.01 g sensitivity; AL204; Mettler Toledo, Shanghai, China) to obtain initial average mass (W0). The specific growth rate (SGR), survival rate (S), average food consumption (FC) of individual, and daily feeding rate (FR) were calculated using the following formulae:
where Wt is the average body weight (g) of live S. intermedius on day t; t is the duration of experiment; N0 is the initial number of live S. intermedius; Nt is the number of live S. intermedius on day t; TBt is the bait supplied on days t; and RBt is the total amount of remaining bait on day t (Qin et al., 2011 ; Chang et al., 2016 (link)).
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4

Leaf Trait Measurement Protocol

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We measured SLA(cm2 g−1) for each individual as the area of fresh leaves divided by their oven-dry mass. To determine this, each leaf was excised, and the petiole was removed. Individual leaflets were used for species with compound leaves. We used a scanner to scan fresh leaves at 300 d.p.i. resolution, and the ImageJ (National Institutes of Health) to measure the leaf area. Leaves were then oven-dried at 80 °C for at least 48 h to a constant value, and dry weight was measured with a balance with a precision of 0.0001 g (Mettler Toledo, AL204, Shanghai, China).
We measured leaf thickness (LT, μm) with paraffin-embedded leaf tissue sections. This process included the following steps: dehydration, wax immersion, embedding, sectioning to a thickness of 8–12 μm, safranin staining and sealing. We then used a light microscope (Leica Microsystems Ltd, Leica DM2500) with a mounted digital camera to take images at 50×, 100×, 200× and 400× magnification (2560 × 1920 pixels). Five images of each slide were taken at each magnification. We then used ImageJ software (National Institutes of Health) to determine the LT. Leaf density (LD, kg m−3) was calculated as 1/(SLA × LT).
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5

Silicone Tube Infusion Dynamics

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Five samples of 20-cm Tygon tube (14-171-219, Saint-Gobain Tygon S3 TM 3603 Flexible Tubings, Fisher Scientific, USA) or silicone tube (8060-0030, NalgeneTM 50 Platinum-cured Silicone Tubing, Thermo Scientific, USA) was utilized in weight measurement. Weight of the tubes prior to infusion were measured with an Analytical Balance (AL204, Analytical Balance, Mettler Toledo, Germany). After the measurement of the initial weights, the tubes were submerged in silicone oil (DMS-T15, polydimethylsiloxane, trimethylsiloxy, 50 cSt, GelestSInc, USA) and weighed at designated time points. For each time point, tubes were removed from the oil with forceps and held vertically for 30 s for the excess silicone oil to flow out of the tube. The bottoms of the tubes were then gently dabbed with Kimwipes (Kimwipe, Kimberly-Clark Corp., USA). After measurement, the tubes were again submerged in silicone oil until the next time point. Tubes were measured every 3 hr for the first 2 days; every 6 hr from days 3 to 6; and every 24 hr from day 6 and onwards. Measurements were taken until data showed no significant increase, and that the plateau trendline consist of at least three data points. Based on these data, for all the protein- and microbial-binding assays, silicone catheters were submerged in silicone oil for 5 days prior to use to ensure full infusion.
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6

PM2.5 Exposure in Pregnant Rats

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Twenty pregnant rats were randomly assigned to 2 groups: 10 in the PM2.5 exposure group and 10 in the control group. Rats in the PM2.5 exposure group received a low PM2.5 dose (15 mg/kg) with intratracheal instillation at day 10 and day 18. The cumulative dose of PM2.5 for the PM2.5 exposure group was 30 mg/kg. Rats in the control group received an equivalent volume of normal saline with intratracheal instillation on the same days. All the pregnant rats received cesarean section at 23 h after the last intratracheal instillation and were sacrificed with anesthesia. All fetuses were weighed on an electronic balance scale (Mettler Toledo, AL204) and morphologically evaluated.
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7

Diurnal Patterns of Water Status

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In the early morning (3:30–5:00) and at noon (11:30–13:00) (both local times) on consecutive sunny days, the water content (WC) and water potential (ψ) were determined. The branches were collected from the middle and upper parts of the canopy on the sunny side, and the ψ of each time period was measured (three times for each branch) using the WP4C Dewpoint Potential Meter. At the same time as ψ determination, the assimilation branches and their corresponding secondary branches (the definition of branch rank) were classified following Strahler’s system (Mcmahon and Kronauer 1976 ). The terminal is the zeroth-grade branch of the current year, and the downward branch is, in turn, the first-grade branch. An appropriate amount of sample was separated and cut from different branches and placed a 1/10 000 precision balance (AL204, METTLER TOLEDO, CHN) to determine the fresh weight (FW). Samples were placed in envelope bags and numbered. They were exposed to sunlight for 4 h in the field and brought back to the laboratory after finishing. Finally, they were dried in an oven at 75 °C for 48 h and weighed to determine the DW. Water content was calculated as follows: WC = (FW − DW)/FW.
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8

Solar Vapor Generation Protocol

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The solar vapor generation experiment was performed by using a 300 W xenon lamp (CEL-S500/350, CEAULIGHT, Beijing, China) as simulated sunlight. The light intensity was adjusted by tuning the distance between light source and material surface to ensure the output of 1 kW m−2 (one standard sunlight) irradiation. The light intensity was measured with a solar power meter (CEL-FZ-A). HCC of 3 mm thickness was cut into rectangular pieces with an area of 4 cm × 1.5 cm, and each piece was put on top of a PS foam of the same size. Mass loss caused by water evaporation under 1 kW m−2 sunlight was measured using an electronic balance (AL204, METTLER TOLEDO, Shanghai, China) at 10-min intervals. The environment temperature was maintained at 20 °C, and relative humidity was ~60%. All evaporation rates were measured after a stabilization period of 30 min. The solar–vapor conversion efficiency (η) was calculated using Formula (3) [27 (link)]: η=m˙HeP0
where m˙ is the mass flux (after subtracting the mass flux of water evaporation under dark environment), He is the equivalent evaporation enthalpy of HCC in pure water, which was calculated as shown in Formula (4) below [18 (link)], and P0 is the solar radiation power (1 kW m−2).
Uin=Hvm0=Hemg
where Uin is the identical power input, Hv and m0 are the evaporation enthalpy and mass change in bulk water, and mg is the mass change in HCC.
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9

Peanut Protein Isolate Characterization

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Peanut protein isolate (S31067, BR grade) was obtained from Shanghai Yuanye Bio-Technology Co., Ltd. (Shanghai, China); Rhodamine B (BS) was purchased from Beijing Yinghai Fine Chemical Industry (Beijing, China).
Rheometer (AR2000 ex, TA Instruments Company, USA), confocal scanning microscope (LEICA TCS SP5 II, Germany LEICA instruments, Germany), magnetic stirrer (85-2, Jiangsu Jintan Jingda Instrument, China), and analytical balance (AL 204, Mettler-Toledo (Switzerland) were used for sample tests.
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10

Preparation and Characterization of Deep Eutectic Solvents

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The DESs were prepared by direct mixing of salts and HBDs according to the specified molar ratio. Each salt was mixed with the corresponding HBD using magnetic stirring at 400 rpm and 353.15 K until a homogenous transparent liquid is formed. Afterward, the mixture was placed in a moisture-controlled area to cool down at room temperature. The weight of the materials was determined by analytical balance (Mettler Toledo AL204) with the standard uncertainty of 10−4 g. The water content of all DESs was determined by Karl-Fischer titration analysis (Aquamax Karl-Fischer titration, GR Scientific Ltd.), resulting in mass fractions of < 1200 ± 100 ppm for all DESs. The DESs prepared with different salt to HBD molar rations are summarized in Table 2.
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