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Keywords = scale parameter pre-estimation

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27 pages, 9621 KiB  
Article
Estimating and Modeling Pinus contorta Transpiration in a Montane Meadow Using Sap-Flow Measurements
by Simon Marks, Christopher Surfleet and Bwalya Malama
Forests 2024, 15(10), 1786; https://doi.org/10.3390/f15101786 - 11 Oct 2024
Viewed by 580
Abstract
This study quantifies the transpiration of encroached lodgepole pine (Pinus contorta var. murryana (Grev. & Balf.) Engelm.) in a montane meadow using pre-restoration sap-flow measurements. Lodgepole pine transpiration and its response to environmental variables were examined in Rock Creek Meadow (RCM), Southern [...] Read more.
This study quantifies the transpiration of encroached lodgepole pine (Pinus contorta var. murryana (Grev. & Balf.) Engelm.) in a montane meadow using pre-restoration sap-flow measurements. Lodgepole pine transpiration and its response to environmental variables were examined in Rock Creek Meadow (RCM), Southern Cascade Range, CA, USA. Sap-flow data from lodgepole pines were scaled to the meadow using tree survey data and then validated with MODIS evapotranspiration estimates for the 2019 and 2020 growing seasons. A modified Jarvis–Stewart model calibrated to 2020 sap-flow data analyzed lodgepole pine transpiration’s correlation with solar radiation, air temperature, vapor pressure deficit, and soil volumetric water content. Model validation utilized 2021 growing season sap-flow data. Calibration and validation employed a Markov Chain Monte Carlo (MCMC) approach through the DREAM(ZS) algorithm with a generalized likelihood (GL) function, enabling parameter and total uncertainty assessment. The model’s scaling was compared with simple scaling estimates. Average lodgepole pine transpiration at RCM ranged between 220.6 ± 25.3 and 393.4 ± 45.7 mm for the campaign (mid-July 2019 to mid-August 2020) and 100.2 ± 11.5 to 178.8 ± 20.7 mm for the 2020 partial growing season (April to mid-August), akin to MODIS ET. The model aligned well with observed normalized sap-velocity during the 2020 growing season (RMSE = 0.087). However, sap-velocity, on average, was underpredicted by the model (PBIAS = −6.579%). Model validation mirrored calibration in performance metrics (RMSE = 0.1233; PBIAS = −2.873%). The 95% total predictive uncertainty confidence intervals generated by GL-DREAM(ZS) enveloped close to the theoretically expected 95% of total observations for the calibration (94.5%) and validation (81.8%) periods. The performance of the GL-DREAM(ZS) approach and uncertainty assessment in this study shows promise for future MJS model applications, and the model-derived 2020 transpiration estimates highlight the MJS model utility for scaling sap-flow measurements from individual trees to stands of trees. Full article
(This article belongs to the Section Forest Ecophysiology and Biology)
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Figure 1

Figure 1
<p>RCM near Chester, CA, including measurement locations. The sap-flow plot insert, displayed at a larger scale, shows the locations for the eight lodgepole pine (<span class="html-italic">Pinus contorta var. murryana</span> (Grev. &amp; Balf.) Engelm.) (LP) instrumented for sap-flow measurement.</p>
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<p>(<b>a</b>) Bark depth (D<sub>b</sub>) versus diameter at breast height (DBH) and (<b>b</b>) sapwood depth (D<sub>s</sub>) versus DBH in log–log space, both including simple linear regressions equation, R2, and line of best fit. Data (<span class="html-italic">n</span> = 47) in (<b>a</b>,<b>b</b>) are from cored trees sampled in the 10 random sample plots.</p>
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<p>(<b>a</b>) 30 min average sap-velocity and daily average daytime and nighttime sap-velocity; (<b>b</b>) daily total precipitation; (<b>c</b>) average daily VPD; and (<b>d</b>) average daily incoming solar radiation and air temperature.</p>
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<p>Hourly <math display="inline"><semantics> <mrow> <msub> <mrow> <mover accent="true"> <mrow> <mi>v</mi> </mrow> <mo>¯</mo> </mover> </mrow> <mrow> <mi>s</mi> <mo>,</mo> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math> response to environmental drivers for the calibration period: (<b>a</b>) <math display="inline"><semantics> <mrow> <msub> <mrow> <mover accent="true"> <mrow> <mi>v</mi> </mrow> <mo>¯</mo> </mover> </mrow> <mrow> <mi>s</mi> <mo>,</mo> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math> vs. solar radiation with different values of VPD; (<b>b</b>) <math display="inline"><semantics> <mrow> <msub> <mrow> <mover accent="true"> <mrow> <mi>v</mi> </mrow> <mo>¯</mo> </mover> </mrow> <mrow> <mi>s</mi> <mo>,</mo> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math> vs. VPD with different values of VWC; (<b>c</b>) <math display="inline"><semantics> <mrow> <msub> <mrow> <mover accent="true"> <mrow> <mi>v</mi> </mrow> <mo>¯</mo> </mover> </mrow> <mrow> <mi>s</mi> <mo>,</mo> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math> vs. air temperature with different values of VWC; and (<b>d</b>) <math display="inline"><semantics> <mrow> <msub> <mrow> <mover accent="true"> <mrow> <mi>v</mi> </mrow> <mo>¯</mo> </mover> </mrow> <mrow> <mi>s</mi> <mo>,</mo> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math> vs. VWC with different values of air temperature.</p>
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<p>Hourly <math display="inline"><semantics> <mrow> <msub> <mrow> <mover accent="true"> <mrow> <mi>v</mi> </mrow> <mo>¯</mo> </mover> </mrow> <mrow> <mi>s</mi> <mo>,</mo> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math> response to environmental drivers for the validation period: (<b>a</b>) <math display="inline"><semantics> <mrow> <msub> <mrow> <mover accent="true"> <mrow> <mi>v</mi> </mrow> <mo>¯</mo> </mover> </mrow> <mrow> <mi>s</mi> <mo>,</mo> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math> vs. solar radiation with different values of VPD; (<b>b</b>) <math display="inline"><semantics> <mrow> <msub> <mrow> <mover accent="true"> <mrow> <mi>v</mi> </mrow> <mo>¯</mo> </mover> </mrow> <mrow> <mi>s</mi> <mo>,</mo> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math> vs. VPD with different values of VWC; (<b>c</b>) <math display="inline"><semantics> <mrow> <msub> <mrow> <mover accent="true"> <mrow> <mi>v</mi> </mrow> <mo>¯</mo> </mover> </mrow> <mrow> <mi>s</mi> <mo>,</mo> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math> vs. air temperature with different values of VWC; and (<b>d</b>) <math display="inline"><semantics> <mrow> <msub> <mrow> <mover accent="true"> <mrow> <mi>v</mi> </mrow> <mo>¯</mo> </mover> </mrow> <mrow> <mi>s</mi> <mo>,</mo> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math> vs. VWC with different values of air temperature.</p>
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<p>MJS predicted vs. observed normalized average sap-velocity for the (<b>a</b>) calibration period (y = 0.022 + 0.88x, R<sup>2</sup> = 0.89) and (<b>b</b>) validation period (y = 0.033 + 0.9x, R<sup>2</sup> = 0.89), including 1:1 line (dashed green) and SLR line (blue).</p>
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<p>Ninety-five percent parameter uncertainty confidence interval and normalized average sap-velocity observations (red points) for (<b>a</b>) calibration and (<b>b</b>) validation periods. Gaps in the time series represent observation data that were removed from the analysis due to precipitation or it being nighttime. Insets show 10 days of sap-velocity observations, corresponding to 95% confidence parameter uncertainty interval for each period.</p>
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<p>Ninety-five percent total predictive uncertainty confidence interval and normalized average sap-velocity observations (blue and red points) for (<b>a</b>) calibration and (<b>b</b>) periods. Insets show 10 days of sap-velocity observations, corresponding to 95% confidence parameter uncertainty interval for each period.</p>
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<p>Daily average transpiration (T) estimated for the random plots in the (<b>a</b>) east stratum and (<b>b</b>) west stratum by sap-velocity radial profile. Ribbons represent ± 1 standard error of the daily mean.</p>
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<p>Time series of 8-day composite MODIS ET estimates compared with 8-day composite lodgepole pine transpiration (T) estimates by sap-velocity radial profile for (<b>a</b>) RCM, (<b>b</b>) east stratum, and (<b>c</b>) west stratum. Ribbons represent ±1 standard deviation of the MODIS ET 8-day composite, weighted mean.</p>
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<p>Time series of residuals between 8-day composite MODIS ET estimates and 8-day composite lodgepole pine transpiration (T) estimates by sap-velocity radial profile for (<b>a</b>) RCM, (<b>b</b>) east stratum, and (<b>c</b>) west stratum.</p>
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<p>Comparison of daily transpiration (T) estimates informed by calibrated MJS model and simple scaling for soil moisture set-up containing plots: (<b>a</b>) SFP (RCSM2b), (<b>b</b>) RCSM1, (<b>c</b>) RCSM3, and (<b>d</b>) RCSM5. The vertical dashed lines mark when VWC dropped below 0.184 during the period shown. Note the differences in vertical scale used for (<b>a</b>–<b>d</b>).</p>
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20 pages, 23235 KiB  
Article
A Cross-Resolution Surface Net Radiative Inversion Based on Transfer Learning Methods
by Shuqi Miao, Qisheng He, Liujun Zhu, Mingxiao Yu, Yuhan Gu and Mingru Zhou
Remote Sens. 2024, 16(13), 2450; https://doi.org/10.3390/rs16132450 - 3 Jul 2024
Viewed by 999
Abstract
Net radiation (Rn) is a key component of the Earth’s energy balance. With the rise of deep learning technology, remote sensing technology has made significant progress in the acquisition of large-scale surface parameters. However, the generally low spatial resolution of net radiation data [...] Read more.
Net radiation (Rn) is a key component of the Earth’s energy balance. With the rise of deep learning technology, remote sensing technology has made significant progress in the acquisition of large-scale surface parameters. However, the generally low spatial resolution of net radiation data and the relative scarcity of surface flux site data at home and abroad limit the potential of deep learning methods in constructing high spatial resolution net radiation models. To address this challenge, this study proposes an innovative approach of a multi-scale transfer learning framework, which assumes that composite models at different spatial scales are similar in structure and parameters, thus enabling the training of accurate high-resolution models using fewer samples. In this study, the Heihe River Basin was taken as the study area and the Rn products of the Global Land Surface Satellite (GLASS) were selected as the target for coarse model training. Based on the dense convolutional network (DenseNet) architecture, 25 deep learning models were constructed to learn the spatial and temporal distribution patterns of GLASS Rn products by combining multi-source data, and a 5 km coarse resolution net radiation model was trained. Subsequently, the parameters of the pre-trained coarse-resolution model were fine-tuned with a small amount of measured ground station data to achieve the transfer from the 5 km coarse-resolution model to the 1 km high-resolution model, and a daily high-resolution net radiation model with 1 km resolution for the Heihe River Basin was finally constructed. The results showed that the bias, R2, and RMSE of the high-resolution net radiation model obtained by transfer learning were 0.184 W/m2, 0.924, and 24.29 W/m2, respectively, which was better than those of the GLASS Rn products. The predicted values were highly correlated with the measured values at the stations and the fitted curves were closer to the measured values at the stations than those of the GLASS Rn products, which further demonstrated that the transfer learning method could capture the soil moisture and temporal variation of net radiation. Finally, the model was used to generate 1 km daily net radiation products for the Heihe River Basin in 2020. This study provides new perspectives and methods for future large-scale and long-time-series estimations of surface net radiation. Full article
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<p>Elevation information for the study area and spatial distribution of eddy flux observatories (dots indicate observatories).</p>
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<p>Structure of the densely connected network (<b>a</b>) and dense blocks (<b>b</b>). BN, Dense, and ReLU in the figure are the fully connected dense layer and the bulk normalized activation layer ReLU, respectively. The model contained d dense blocks with w neurons in each dense layer. The input data were fed into the model in a sequential manner, with each input record containing 11 values, which were processed one by one in a given order.</p>
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<p>A net radiative transfer learning framework based on dense convolutional networks was implemented to optimize 25 densely connected networks for 1 km net radiative inversion by a fine-tuning method. In the figure, <span class="html-italic">d</span> and <span class="html-italic">w</span> refer to the number of densely connected blocks and the number of neurons, respectively.</p>
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<p>Flowchart of this study.</p>
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<p>Training accuracy of 25 coarse resolution models, with based <span class="html-italic">d</span>(1, 2, 3, 4, 5) and <span class="html-italic">w</span>(8, 16, 32, 64, 128) being the number of dense blocks and the width of each dense layer. (<b>a</b>) DenseNet−1−8; (<b>b</b>) DenseNet−1−16; (<b>c</b>) DenseNet−1−32; (<b>d</b>) DenseNet−1−64; (<b>e</b>) DenseNet−1−128; (<b>f</b>) DenseNet−2−8; (<b>g</b>) DenseNet−2−16; (<b>h</b>) DenseNet−2−32; (<b>i</b>) DenseNet−2−64; (<b>j</b>) DenseNet−2−128; (<b>k</b>) DenseNet−3−8; (<b>l</b>) DenseNet−3−16; (<b>m</b>) DenseNet−3−32; (<b>n</b>) DenseNet−3−64; (<b>o</b>) DenseNet−3−128; (<b>p</b>) DenseNet−4−8; (<b>q</b>) DenseNet−4−16; (<b>r</b>) DenseNet−4−32; (<b>s</b>) DenseNet−4−64; (<b>t</b>) DenseNet−4−128; (<b>u</b>) DenseNet−5−8; (<b>v</b>) DenseNet−8−16; (<b>w</b>) DenseNet−5−32; (<b>x</b>) DenseNet−5−64; (<b>y</b>) DenseNet−5−128. The different color lines represent different meanings, there are 1:1 lines, and fitting lines, through the two lines, you can determine the effectiveness and accuracy of the model training.</p>
Full article ">Figure 5 Cont.
<p>Training accuracy of 25 coarse resolution models, with based <span class="html-italic">d</span>(1, 2, 3, 4, 5) and <span class="html-italic">w</span>(8, 16, 32, 64, 128) being the number of dense blocks and the width of each dense layer. (<b>a</b>) DenseNet−1−8; (<b>b</b>) DenseNet−1−16; (<b>c</b>) DenseNet−1−32; (<b>d</b>) DenseNet−1−64; (<b>e</b>) DenseNet−1−128; (<b>f</b>) DenseNet−2−8; (<b>g</b>) DenseNet−2−16; (<b>h</b>) DenseNet−2−32; (<b>i</b>) DenseNet−2−64; (<b>j</b>) DenseNet−2−128; (<b>k</b>) DenseNet−3−8; (<b>l</b>) DenseNet−3−16; (<b>m</b>) DenseNet−3−32; (<b>n</b>) DenseNet−3−64; (<b>o</b>) DenseNet−3−128; (<b>p</b>) DenseNet−4−8; (<b>q</b>) DenseNet−4−16; (<b>r</b>) DenseNet−4−32; (<b>s</b>) DenseNet−4−64; (<b>t</b>) DenseNet−4−128; (<b>u</b>) DenseNet−5−8; (<b>v</b>) DenseNet−8−16; (<b>w</b>) DenseNet−5−32; (<b>x</b>) DenseNet−5−64; (<b>y</b>) DenseNet−5−128. The different color lines represent different meanings, there are 1:1 lines, and fitting lines, through the two lines, you can determine the effectiveness and accuracy of the model training.</p>
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<p>Scatter plots of net radiation estimation accuracy. (<b>a</b>) Pre-trained coarse model site validation scatter plot of accuracy. (<b>b</b>) GLASS Rn product site validation scatter plot of accuracy. (<b>c</b>) Fine-tuned transfer learning model site validation scatter plot of accuracy.</p>
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<p>Time series plot of Rn with GLASS using in situ measurements at sites and based on fine-tuning transfer learning approach. (<b>a</b>) A’rou station (Grassland); (<b>b</b>) Daman (Cropland); (<b>c</b>) Dashalong station (Grassland); (<b>d</b>) Huazhaizi station (Desert); (<b>e</b>) Desert station (Desert); (<b>f</b>) Mixed forest station (Mixed forest); (<b>g</b>) Jingyangling station (Grassland); (<b>h</b>) Sidaoqiao station (Shrubs); (<b>i</b>) Yakou station (Grassland); (<b>j</b>) Zhangye wetland station (Wetland).</p>
Full article ">Figure 7 Cont.
<p>Time series plot of Rn with GLASS using in situ measurements at sites and based on fine-tuning transfer learning approach. (<b>a</b>) A’rou station (Grassland); (<b>b</b>) Daman (Cropland); (<b>c</b>) Dashalong station (Grassland); (<b>d</b>) Huazhaizi station (Desert); (<b>e</b>) Desert station (Desert); (<b>f</b>) Mixed forest station (Mixed forest); (<b>g</b>) Jingyangling station (Grassland); (<b>h</b>) Sidaoqiao station (Shrubs); (<b>i</b>) Yakou station (Grassland); (<b>j</b>) Zhangye wetland station (Wetland).</p>
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<p>Spatial distribution of 2020 net surface radiation in the Heihe River Basin. Figures (<b>a</b>,<b>c</b>,<b>e</b>,<b>g</b>) show GLASS Rn products; figures (<b>b</b>,<b>d</b>,<b>f</b>,<b>h</b>) show net radiation products based on transfer learning.</p>
Full article ">Figure 8 Cont.
<p>Spatial distribution of 2020 net surface radiation in the Heihe River Basin. Figures (<b>a</b>,<b>c</b>,<b>e</b>,<b>g</b>) show GLASS Rn products; figures (<b>b</b>,<b>d</b>,<b>f</b>,<b>h</b>) show net radiation products based on transfer learning.</p>
Full article ">Figure 8 Cont.
<p>Spatial distribution of 2020 net surface radiation in the Heihe River Basin. Figures (<b>a</b>,<b>c</b>,<b>e</b>,<b>g</b>) show GLASS Rn products; figures (<b>b</b>,<b>d</b>,<b>f</b>,<b>h</b>) show net radiation products based on transfer learning.</p>
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<p>Spatial distribution of daily average surface net radiation in the Heihe River Basin in 2020.</p>
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<p>Relative importance of net radiation model predictors.</p>
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18 pages, 26335 KiB  
Article
Revealing the Eco-Environmental Quality of the Yellow River Basin: Trends and Drivers
by Meiling Zhou, Zhenhong Li, Meiling Gao, Wu Zhu, Shuangcheng Zhang, Jingjing Ma, Liangyu Ta and Guijun Yang
Remote Sens. 2024, 16(11), 2018; https://doi.org/10.3390/rs16112018 - 4 Jun 2024
Cited by 3 | Viewed by 1139
Abstract
The Yellow River Basin (YB) acts as a key barrier to ecological security and is an important experimental region for high-quality development in China. There is a growing demand to assess the ecological status in order to promote the sustainable development of the [...] Read more.
The Yellow River Basin (YB) acts as a key barrier to ecological security and is an important experimental region for high-quality development in China. There is a growing demand to assess the ecological status in order to promote the sustainable development of the YB. The eco-environmental quality (EEQ) of the YB was assessed at both the regional and provincial scales utilizing the remote sensing-based ecological index (RSEI) with Landsat images from 2000 to 2020. Then, the Theil–Sen (T-S) estimator and Mann–Kendall (M-K) test were utilized to evaluate its variation trend. Next, the optimal parameter-based geodetector (OPGD) model was used to examine the drivers influencing the EEQ in the YB. Finally, the geographically weighted regression (GWR) model was utilized to further explore the responses of the drivers to RSEI changes. The results suggest that (1) a lower RSEI value was found in the north, while a higher RSEI value was found in the south of the YB. Sichuan (SC) and Inner Mongolia (IM) had the highest and the lowest EEQ, respectively, among the YB provinces. (2) Throughout the research period, the EEQ of the YB improved, whereas it deteriorated in both Henan (HA) and Shandong (SD) provinces. (3) The soil-available water content (AWC), annual precipitation (PRE), and distance from impervious surfaces (IMD) were the main factors affecting the spatial differentiation of RSEI in the YB. (4) The influence of meteorological factors (PRE and TMP) on RSEI changes was greater than that of IMD, and the influence of IMD on RSEI changes showed a significant increasing trend. The research results provide valuable information for application in local ecological construction and regional development planning. Full article
(This article belongs to the Special Issue Environmental Monitoring Using Satellite Remote Sensing)
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Graphical abstract

Graphical abstract
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<p>Location of the YB.</p>
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<p>Technology flowchart.</p>
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<p>Spatial distribution of driving factors.</p>
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<p>Spatial distribution of RSEI in YB.</p>
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<p>The proportion of RSEI classes in YB provinces (<b>a</b>) and land cover types (<b>b</b>). From left to right, the figure represents the years 2000, 2005, 2010, 2015, and 2020, respectively.</p>
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<p>Spatial distribution of RSEI change characteristics during the period of 2000–2020.</p>
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<p>Interactive detection matrix in YB. * represents nonlinear enhancement; otherwise, there is bilinear enhancement.</p>
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<p>q statistic of factor detection of nine provinces in YB (95% confidence level).</p>
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<p>Distribution of regression coefficients of the GWR model.</p>
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<p>The proportion of the dominant driving factors in the YB and its provinces. From left to right, the figure represents 2000–2005, 2005–2010, 2010–2015, 2015–2020, and 2000–2020, respectively.</p>
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<p>Christmas tree anomaly (<b>a</b>) and caterpillar tracks (<b>b</b>).</p>
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<p>Correlation coefficient r between indicators.</p>
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<p>Mean RSEI values for different land cover types.</p>
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<p>Area changes of different land cover types in YB from 2000 to 2020.</p>
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17 pages, 3928 KiB  
Article
Computer Vision System Based on the Analysis of Gait Features for Fall Risk Assessment in Elderly People
by Rogelio Cedeno-Moreno, Diana L. Malagon-Barillas, Luis A. Morales-Hernandez, Mayra P. Gonzalez-Hernandez and Irving A. Cruz-Albarran
Appl. Sci. 2024, 14(9), 3867; https://doi.org/10.3390/app14093867 - 30 Apr 2024
Viewed by 1299
Abstract
Up to 30% of people over the age of 60 are at high risk of falling, which can cause injury, aggravation of pre-existing conditions, or even death, with up to 684,000 fatal falls reported annually. This is due to the difficult task of [...] Read more.
Up to 30% of people over the age of 60 are at high risk of falling, which can cause injury, aggravation of pre-existing conditions, or even death, with up to 684,000 fatal falls reported annually. This is due to the difficult task of establishing a preventive system for the care of the elderly, both in the hospital environment and at home. Therefore, this work proposes the development of an intelligent vision system that uses a novel methodology to infer fall risk from the analysis of kinetic and spatiotemporal gait parameters. In general, each patient is assessed using the Tinetti scale. Then, the computer vision system estimates the biomechanics of walking and obtains gait features, such as stride length, cadence, period, and range of motion. Subsequently, this information serves as input to an artificial neural network that diagnoses the risk of falling. Ninety-six participants took part in the study. The system’s performance was 99.1% accuracy, 94.4% precision, 96.9% recall, 99.4% specificity, and 95.5% F1-Score. Thus, the proposed system can evaluate the fall risk assessment, which could benefit clinics, hospitals, and even homes by allowing them to assess in real time whether a person is at high risk of falling to provide timely assistance. Full article
(This article belongs to the Special Issue Advanced Sensors for Postural or Gait Stability Assessment)
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<p>Methodology general diagram for the development of the fall risk assessment system.</p>
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<p>Workspace and vision system setup.</p>
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<p>Gait image labeling.</p>
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<p>Pose estimation via key point detection derived from frame analysis.</p>
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<p>Detection of knee angle during heel strike (black dots) and toe-off (red dots). (<b>A</b>) Right ankle displacement along the <span class="html-italic">x</span>-axis. (<b>B</b>) Right knee angle.</p>
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<p>Division of the signals into 5 s windows, visually represented by the signal shown in blue and the divisions in red.</p>
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<p>The final structure of the fall risk assessment ANN.</p>
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<p>Graphs obtained from the training and validation of the ANN. (<b>A</b>). Loss. (<b>B</b>). Accuracy.</p>
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<p>Confusion matrix of the fall risk assessment algorithm.</p>
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<p>Validation of fall risk classification using a confusion matrix.</p>
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20 pages, 31267 KiB  
Article
A Training-Free Estimation Method for the State of Charge and State of Health of Series Battery Packs under Various Load Profiles
by Lei Pei, Cheng Yu, Tiansi Wang, Jiawei Yang and Wanlin Wang
Energies 2024, 17(8), 1824; https://doi.org/10.3390/en17081824 - 11 Apr 2024
Viewed by 907
Abstract
To ensure the accuracy of state of charge (SOC) and state of health (SOH) estimation for battery packs while minimizing the amount of pre-experiments required for aging modeling and the scales of computation for online management, a decisive-cell-based estimation method with training-free characteristic [...] Read more.
To ensure the accuracy of state of charge (SOC) and state of health (SOH) estimation for battery packs while minimizing the amount of pre-experiments required for aging modeling and the scales of computation for online management, a decisive-cell-based estimation method with training-free characteristic parameters and a dynamic-weighted estimation strategy is proposed in this paper. Firstly, to reduce the computational complexity, the state estimation of battery packs is summed up to that of two decisive cells, and a new selection approach for the decisive cells is adopted based on the detection of steep voltage changes. Secondly, two novel ideas are implemented for the state estimation of the selected cells. On the one hand, a set of characteristic parameters that only exhibit local curve shrinkage with aging is chosen, which keeps the corresponding estimation approaches away from training. On the other hand, multiple basic estimation approaches are effectively combined by their respective dynamic weights, which ensures the estimation can maintain a good estimation accuracy under various load profiles. Finally, the experimental results show that the new method can quickly correct the initial setting deviations and have a high estimation accuracy for both the SOC and SOH within 2% for a series battery pack consisting of cells with obvious inconsistency. Full article
(This article belongs to the Section L: Energy Sources)
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<p>The state estimation of battery packs.</p>
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<p>The OCV changes with battery aging at the vehicle stage.</p>
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<p>The specific experimental process.</p>
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<p>The OCV curves at different aging degrees and different temperatures. (<b>a</b>) The OCV curves at SOH = 1, 0.95 and 0.9. (<b>b</b>) The OCV curves at 10 °C, 25 °C and 40 °C.</p>
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<p>The DEV curves at different aging degrees and different temperatures. (<b>a</b>) The DEV curves at SOH = 1, 0.95 and 0.9. (<b>b</b>) The DEV curves at 10 °C, 25 °C and 40 °C.</p>
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<p>The SEV curves at different temperatures and different charge rates. (<b>a</b>) SEV curves at different charge rates at 10 °C. (<b>b</b>) Aligned SEV curves at different charge rates at 10 °C. (<b>c</b>) SEV curves at different charge rates at 25 °C. (<b>d</b>) Aligned SEV curves at different charge rates at 25 °C. (<b>e</b>) SEV curves at different charge rates at 40 °C. (<b>f</b>) Aligned SEV curves at different charge rates at 40 °C.</p>
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<p>The SEV curves at the same charge rate (1.00 C) and different aging degrees. (<b>a</b>) SEV curves at different aging degrees. (<b>b</b>) Aligned SEV curves at different aging degrees.</p>
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<p>The SEV curves at the same rate and different temperatures. (<b>a</b>) The SEV curves at different temperatures. (<b>b</b>) The aligned SEV curves at different temperatures.</p>
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<p>The voltage and current curves of cells in series battery packs.</p>
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<p>The SOC estimation and dynamic weight results. (<b>a</b>) The SOC in the coulomb counting method. (<b>b</b>) The proportion of the weight in the total weight for the coulomb counting method. (<b>c</b>) The SOC in the OCV method. (<b>d</b>) The proportion of the weight in the total weight for the OCV method. (<b>e</b>) The SOC in the equivalent circuit method. (<b>f</b>) The proportion of the weight in the total weight for the equivalent circuit method. (<b>g</b>) The SOC in the charging matching method. (<b>h</b>) The proportion of the weight in the total weight for the charging matching method.</p>
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<p>The results of the SOC and SOH estimation. (<b>a</b>) The results of the SOC estimation. (<b>b</b>) The results of the SOH estimation.</p>
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<p>The selection of decisive cells.</p>
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<p>The SOC estimation results for battery packs. (<b>a</b>) Comparison of the SOC results for battery packs. (<b>b</b>)The error of the SOC estimation for battery packs.</p>
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<p>The SOH estimation results for battery packs. (<b>a</b>) Comparison of the SOH results for battery packs. (<b>b</b>)The error of the SOH estimation for battery packs.</p>
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16 pages, 2971 KiB  
Technical Note
Arctic Greening Trends: Change Points in Satellite-Derived Normalized Difference Vegetation Indexes and Their Correlation with Climate Variables over the Last Two Decades
by Minji Seo and Hyun-Cheol Kim
Remote Sens. 2024, 16(7), 1160; https://doi.org/10.3390/rs16071160 - 27 Mar 2024
Viewed by 1137
Abstract
In this study, we utilized NDVI data from the moderate resolution imaging spectroradiometer (MODIS) alongside climatic variables obtained from a reanalyzed dataset to analyze Arctic greening during the summer months (June–September) of the last two decades. This investigation entailed a detailed analysis of [...] Read more.
In this study, we utilized NDVI data from the moderate resolution imaging spectroradiometer (MODIS) alongside climatic variables obtained from a reanalyzed dataset to analyze Arctic greening during the summer months (June–September) of the last two decades. This investigation entailed a detailed analysis of these changes across various temporal scales. The data indicated a continuous trend of Arctic greening, evidenced by a 1.8% per decade increment in the NDVI. Notably, significant change points were identified in June 2012 and September 2013. A comparative assessment of NDVI pre- and post-these inflection points revealed an elongation of the Arctic greening trend. Furthermore, an anomalous increase in NDVI of 2% per decade was observed, suggesting an acceleration in greening. A comprehensive analysis was conducted to decipher the correlation between NDVI, temperature, and energy budget parameters to elucidate the underlying causes of these change points. Although the correlation between these variables was relatively low throughout the summer months, a distinct pattern emerged when these periods were dissected and examined in the context of the identified change points. Preceding the change point, a strong correlation (approximately 0.6) was observed between all variables; however, this correlation significantly diminished after the change point, dropping to less than half. This shift implies an introduction of additional external factors influencing the Arctic greening trend after the change point. Our findings provide foundational data for estimating the tipping point in Arctic terrestrial ecosystems. This is achieved by integrating the observed NDVI change points with their relationship with climatic variables, which are essential in comprehensively understanding the dynamics of Arctic climate change, particularly with alterations in tundra vegetation. Full article
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<p>Distribution of valid percentages per pixel after applying the quality flag; the gray shading indicates the count of valid pixels below 15% during the study period.</p>
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<p>The annual change in NDVI, Arctic greening area, and time series data distribution for the summer periods of 2000–2020: (<b>a</b>) annual NDVI trend, (<b>b</b>) Arctic greening area, and (<b>c</b>) decomposition results of the time series data. The decomposition consists of the trend (red line), the standard deviation of the trend (orange shade), and the residuals (bar plot).</p>
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<p>Monthly NDVI time series data collected under various conditions; (<b>a</b>) trends, (<b>b</b>) growing seasonal cycles before/after change points, and (<b>c</b>) anomalies calculated relative to the starting year.</p>
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<p>Summer climate variable time series data for the tundra; (<b>a</b>) Temperature anomaly (surface air temperature and land surface temperature), (<b>b</b>) Energy budget anomaly (Net radiation, Surface sensible heat flux, Surface latent heat flux), (<b>c</b>) Difference between surface air temperature and land surface temperature, and (<b>d</b>) Bowen ratio.</p>
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<p>Monthly time lag correlations; (<b>a</b>) Surface air temperature, (<b>b</b>) Land surface temperature, (<b>c</b>) Net radiation, (<b>d</b>) Surface sensible heat flux, (<b>e</b>) Surface latent heat flux.</p>
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15 pages, 2479 KiB  
Article
Differential Impact of the Biodegradation Sunflower Oil, Particulate Substrate, Caused by the Presence of Saccharose, Soluble Substrate, on Activated Sludge Treatment
by Pedro Cisterna-Osorio, Miguel Moraga-Chaura, Raydel Manrique-Suárez and Mabel Vega-Coloma
Water 2023, 15(24), 4282; https://doi.org/10.3390/w15244282 - 15 Dec 2023
Viewed by 1531
Abstract
This research studies the biodegradation of sunflower-type vegetative oil in two proposed activated sludge systems, the first one to biologically treat an influent containing only vegetative oil and the second one to treat a mixture of vegetable oil plus saccharose. The purpose of [...] Read more.
This research studies the biodegradation of sunflower-type vegetative oil in two proposed activated sludge systems, the first one to biologically treat an influent containing only vegetative oil and the second one to treat a mixture of vegetable oil plus saccharose. The purpose of these analyses is to evaluate the differential impact caused by the soluble substrate saccharose on the removal of vegetative oil. Vegetative oil biodegradation in both systems was studied and quantified via integral mass balance, and relevant operating parameters were monitored. This experimentation based on the mass balance estimation of biodegraded vegetative oil serves as a reference to understand the effect of soluble substrates present in mixed wastewater on oil biodegradation. Information was generated on the performance of the two activated sludge treatment systems. Both influents were pre-stirred before they entered the bench-scale activated sludge plants. The working range for sunflower oil concentration was 120 to 520 mg/L for the influent with sunflower oil and 180 to 750 mg/L for the influent with sunflower oil and saccharose. Biodegradation was in the order of 56 to 72% and 47 to 67%, respectively. The removal of sunflower oil in biodegradation and flotation was in the order of 90% in both scenarios. Full article
(This article belongs to the Special Issue Biological Technology for Wastewater Treatment)
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<p>Experimental equipment diagram.</p>
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<p>Activated sludge plant process diagram.</p>
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<p>COD removal efficiency and mass loading for oily influent.</p>
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<p>COD removal and biodegradation efficiency and mass loading for mixed influent.</p>
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<p>COD behavior in mixed influent, effluent and effluent plus accumulated effluent.</p>
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<p>Feeding without saccharose. Sunflower oil concentration in influent, effluent and effluent plus accumulated oil and oil removal and biodegradation efficiency.</p>
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<p>Concentration of mixed influent, effluent and effluent plus accumulated effluent.</p>
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<p>Feeding without saccharose. Biomass behavior, MLSSs, MLVSSs and SVI evolution.</p>
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<p>Feeding with saccharose. Biomass behavior, MLTSS, MLVSS and SVI evolution.</p>
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20 pages, 11985 KiB  
Article
Simultaneous Vehicle Localization and Roadside Tree Inventory Using Integrated LiDAR-Inertial-GNSS System
by Xianghua Fan, Zhiwei Chen, Peilin Liu and Wenbo Pan
Remote Sens. 2023, 15(20), 5057; https://doi.org/10.3390/rs15205057 - 21 Oct 2023
Cited by 3 | Viewed by 1894
Abstract
Autonomous driving systems rely on a comprehensive understanding of the surrounding environment, and trees, as important roadside features, have a significant impact on vehicle positioning and safety analysis. Existing methods use mobile LiDAR systems (MLS) to collect environmental information and automatically generate tree [...] Read more.
Autonomous driving systems rely on a comprehensive understanding of the surrounding environment, and trees, as important roadside features, have a significant impact on vehicle positioning and safety analysis. Existing methods use mobile LiDAR systems (MLS) to collect environmental information and automatically generate tree inventories based on dense point clouds, providing accurate geometric parameters. However, the use of MLS systems requires expensive survey-grade laser scanners and high-precision GNSS/IMU systems, which limits their large-scale deployment and results in poor real-time performance. Although LiDAR-based simultaneous localization and mapping (SLAM) techniques have been widely applied in the navigation field, to the best of my knowledge, there has been no research conducted on simultaneous real-time localization and roadside tree inventory. This paper proposes an innovative approach that uses LiDAR technology to achieve vehicle positioning and a roadside tree inventory. Firstly, a front-end odometry based on an error-state Kalman filter (ESKF) and a back-end optimization framework based on factor graphs are employed. The updated poses from the back-end are used for establishing point-to-plane residual constraints for the front-end in the local map. Secondly, a two-stage approach is adopted to minimize global mapping errors, refining accumulated mapping errors through GNSS-assisted registration to enhance system robustness. Additionally, a method is proposed for creating a tree inventory that extracts line features from real-time LiDAR point cloud data and projects them onto a global map, providing an initial estimation of possible tree locations for further tree detection. This method uses shared feature extraction results and data pre-processing results from SLAM to reduce the computational load of simultaneous vehicle positioning and roadside tree inventory. Compared to methods that directly search for trees in the global map, this approach benefits from fast perception of the initial tree position, meeting real-time requirements. Finally, our system is extensively evaluated on real datasets covering various road scenarios, including urban and suburban areas. The evaluation metrics are divided into two parts: the positioning accuracy of the vehicle during operation and the detection accuracy of trees. The results demonstrate centimeter-level positioning accuracy and real-time automatic creation of a roadside tree inventory. Full article
(This article belongs to the Section Environmental Remote Sensing)
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<p>Overvierw of the proposed system.</p>
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<p>LiDAR point cloud.</p>
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<p>Point cloud sequence mapping image.</p>
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<p>Classification and filtering of line feature point cloud set.</p>
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<p>Illustrates the point cloud processing steps for tree detection. The different colors represent varying reflectance intensities of the point cloud data. (<b>a</b>) shows a single frame of raw point cloud data. (<b>b</b>) illustrates the results of extracting line features and plane features from a single frame of raw point cloud data.; (<b>c</b>) shows the trunk detection results after removing ground plane features and performing cluster analysis. In the figure, 1 represents line features, and 2 represents detected tree trunks.</p>
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<p>Illustration of point cloud motion distortion compensation and ESKF prediction time.</p>
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<p>Flowchart of the backend graph optimization algorithm.</p>
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<p>Shows the physical installation and arrangement of the autonomous driving platform vehicle and sensors.</p>
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<p>Shows the visualized map results. (<b>a</b>) represents the trajectory plotted on a satellite map, while (<b>b</b>) represents the original point cloud map.</p>
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<p>Experimental results of single-row trees along the road. (<b>a</b>) Raw point cloud, (<b>b</b>) Extracted trunks, (<b>c</b>) Extracted tree crowns, and (<b>d</b>) Extracted trees.</p>
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<p>The true trajectory and keyframe trajectory in the x, y, and z directions.</p>
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<p>The APE trajectory curve.</p>
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<p>Accuracy comparison of Fast-Lioi and the proposed method.</p>
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16 pages, 3066 KiB  
Article
Industrial Emission Monitoring and Assessment of Air Quality in Karachi Coastal City, Pakistan
by Mohammad Idrees, Yasmin Nergis and Muhammad Irfan
Atmosphere 2023, 14(10), 1515; https://doi.org/10.3390/atmos14101515 - 30 Sep 2023
Cited by 4 | Viewed by 4012
Abstract
Industrialization, anthropogenic activities, the exhaust of vehicles and exponential population growth have a significant impact on the outdoor air quality of megacities across the world. Karachi is one of the largest cities in Pakistan, South Asia. The dense population, rapid economic growth and [...] Read more.
Industrialization, anthropogenic activities, the exhaust of vehicles and exponential population growth have a significant impact on the outdoor air quality of megacities across the world. Karachi is one of the largest cities in Pakistan, South Asia. The dense population, rapid economic growth and unplanned industrial activities have improved the socioeconomic status but also deteriorated the air quality of Karachi. The severe increase in air pollution has become a threat to the local population in terms of their health issues, quality of life and environment. Therefore, it is essential to quantify and monitor the spatiotemporal variation in outdoor air quality parameters. The current study aims to monitor the air quality in four major industrial zones of Karachi for three years (2020–2022). The field data was collected during the periods of post-monsoon and pre-monsoon using the HAZ-SCANNER (HIM-6000) apparatus, which measured outdoor air pollutants such as carbon monoxide (CO), nitrogen oxides (NO2), sulfur dioxide (SO2) and particulate matter (PM10, PM2.5 and TSPM). The data from 24 stations was analyzed using statistical analysis tools to estimate the parameters and Arc GIS to map the spatial variation of each parameter. The result shows that the concentration of particulate matter (TSPM, PM2.5 and PM10), SO2, NO2 and CO values at sampling sites are moderate in the post-monsoon season as compared to the pre-monsoon season due to cyclical monsoon effects and exceed the environmental quality standards. It was also noted that the North Karachi industrial area is at lower risk due to the small-scale industry. The higher levels of air pollutants have numerous health implications and may cause chronic infections. The air pollutant has a severe impact on plant growth and soil. Therefore, it is important to implement local environmental standards regarding outdoor air pollutants to mitigate the adverse impact on human health and economic activities. Full article
(This article belongs to the Section Air Quality)
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<p>Location map for the outdoor air quality monitoring site. (<b>a</b>) Pakistan, (<b>b</b>) Karachi and (<b>c</b>) twenty-four air monitoring stations in four major industrial zones of Karachi.</p>
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<p>Illustration of industrial emission monitoring and outdoor air quality parameter assessment of Karachi, Pakistan.</p>
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<p>Research methodology workflow for air quality analysis impact by industrial emissions.</p>
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<p>Variation in air quality (pre-monsoon and post-monsoon) for monitored parameters at 24 stations in Karachi industrial areas: (<b>a</b>) CO, (<b>b</b>) NO<sub>2</sub>, (<b>c</b>) SO<sub>2</sub>, (<b>d</b>) TSPM, (<b>e</b>) PM<sub>2.5</sub>, and (<b>f</b>) PM<sub>10</sub>.</p>
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<p>Correlation analysis to evaluate the impact of monsoon season on air pollutant levels in Karachi for the collected sample measured in (µg/m<sup>3</sup>) during the pre-monsoon (PMS) on the x-axis and post-monsoon (PtMS) on the y-axis (<b>a</b>) CO, (<b>b</b>) NO<sub>2</sub>, (<b>c</b>) SO<sub>2</sub>, (<b>d</b>) TSPM, (<b>e</b>) PM<sub>2.5</sub>, and (<b>f</b>) PM<sub>10</sub>.</p>
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<p>Pre-monsoon geospatial analysis and visualization of air quality values for NO<sub>2</sub>, SO<sub>2</sub>, CO, TSPM, PM<sub>10</sub> and PM<sub>2.5</sub>.</p>
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<p>Post-monsoon geospatial analysis and visualization using Arc GIS of air quality values for NO<sub>2</sub>, SO<sub>2</sub>, CO, TSPM, PM<sub>10</sub> and PM<sub>2.5</sub>.</p>
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<p>Google Earth map shows that the Karachi industrial zones are surrounded by dense populations without any demarcation between industrial and residential areas (<b>a</b>) S.I.T.E industrial area, (<b>b</b>) Korangi industrial area, (<b>c</b>) Landhi industrial area, and (<b>d</b>) North Karachi industrial area.</p>
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13 pages, 840 KiB  
Article
Optimization of the Heat-Drying Conditions of Drone Pupae by Response Surface Methodology (RSM)
by SeungHee Baek, Agapito Sheryl Mae and InSik Nam
Foods 2023, 12(16), 3062; https://doi.org/10.3390/foods12163062 - 15 Aug 2023
Cited by 1 | Viewed by 1308
Abstract
Recent research has been conducted on various types of pre-processing methods for insects, including freeze-drying, microwave drying, hot air heat drying, and non-heat drying. This study aimed to identify the factors that have the greatest impact on heat drying conditions and establish the [...] Read more.
Recent research has been conducted on various types of pre-processing methods for insects, including freeze-drying, microwave drying, hot air heat drying, and non-heat drying. This study aimed to identify the factors that have the greatest impact on heat drying conditions and establish the optimal heat drying conditions for drone pupae (Apis melifera L.) using response surface methodology (RSM) to minimize quality changes. Drone pupae were treated under various conditions, including blanching time (53–187 s) (X1), drying temperatures (41.6–58.4 °C) (X2), and drying time (266–434 min) (X3). The effect of these treatments on response variables, including the color parameter (WI, YI, BI, △E, and BD), AV, and TB of the dried drone pupae, was evaluated using a central composite design. The whole design consisted of 20 experimental points carried out in random order, which included eight factorial points, six center points, and six axial points. The optimal drying conditions for drone pupae were determined to be a blanching time of 58 s, a drying temperature of 56.7 °C, and a drying time of 298 min. The response variables were most affected by drying temperature and drying time and to a lesser extent by blanching time. The processed drone pupae using the optimized drying conditions resulted in the color parameters (WI, BI, YI, ΔE, and BD) being found to be 66.67, 21.33, 26.27, 31.27 and 0.13, respectively. And TB (log CFU/g) and AV (mg/g) values were found to be 3.12 and 4.33, respectively. The estimated and actual values for dried drone pupae showed no significant difference (p < 0.05). Comparing the physicochemical and microbiological properties of freeze-dried and optimal heat-dried drone pupae, the L and b value as well as PV were significantly lower in the heat-dried samples, while no significant difference was observed in the a value and AV (p < 0.05). Our study suggests that the model we developed can be applied to the large-scale production of drying conditions for use in the pharmaceutical and food industries. Full article
(This article belongs to the Topic Sustainable Food Processing)
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<p>The three-dimensional response surface plots showing interactive effects of blanching time (X<sub>1</sub>), drying temperature (X<sub>2</sub>), and drying time (X<sub>3</sub>) on WI (<b>a</b>), BI (<b>b</b>), YI (<b>c</b>), △E (<b>d</b>), BD (<b>e</b>,<b>f</b>). Each net surface represents the response surface predicted with the quadratic model as a function of each variable and described by the equations given in <a href="#foods-12-03062-t003" class="html-table">Table 3</a>. *: significant at <span class="html-italic">p</span> &lt; 0.05. **: significant at <span class="html-italic">p</span> &lt; 0.01.</p>
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20 pages, 34233 KiB  
Article
Multi-Level Convolutional Network for Ground-Based Star Image Enhancement
by Lei Liu, Zhaodong Niu, Yabo Li and Quan Sun
Remote Sens. 2023, 15(13), 3292; https://doi.org/10.3390/rs15133292 - 27 Jun 2023
Cited by 2 | Viewed by 1273
Abstract
The monitoring of space debris is important for spacecraft such as satellites operating in orbit, but the background in star images taken by ground-based telescopes is relatively complex, including stray light caused by diffuse reflections from celestial bodies such as the Earth or [...] Read more.
The monitoring of space debris is important for spacecraft such as satellites operating in orbit, but the background in star images taken by ground-based telescopes is relatively complex, including stray light caused by diffuse reflections from celestial bodies such as the Earth or Moon, interference from clouds in the atmosphere, etc. This has a serious impact on the monitoring of dim and small space debris targets. In order to solve the interference problem posed by a complex background, and improve the signal-to-noise ratio between the target and the background, in this paper, we propose a novel star image enhancement algorithm, MBS-Net, based on background suppression. Specifically, the network contains three parts, namely the background information estimation stage, multi-level U-Net cascade module, and recursive feature fusion stage. In addition, we propose a new multi-scale convolutional block, which can laterally fuse multi-scale perceptual field information, which has fewer parameters and fitting capability compared to ordinary convolution. For training, we combine simulation and real data, and use parameters obtained on the simulation data as pre-training parameters by way of parameter migration. Experiments show that the algorithm proposed in this paper achieves competitive performance in all evaluation metrics on multiple real ground-based datasets. Full article
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<p>Star image schematics of various backgrounds. (<b>a</b>) Wide cloud layer. (<b>a-1</b>) A 3D grayscale schematic of (<b>a</b>). (<b>b</b>) Uniform background. (<b>b-1</b>) A 3D grayscale schematic of (<b>b</b>). (<b>c</b>) Earth stray light. (<b>c-1</b>) A 3D grayscale schematic of (<b>c</b>). (<b>d</b>) Earth stray light. (<b>d-1</b>) A 3D grayscale schematic of (<b>d</b>). (<b>e</b>) High-speed moving objects in the field of view. (<b>e-1</b>) A 3D grayscale schematic of (<b>e</b>). (<b>f</b>) Moonlight background. (<b>f-1</b>) A 3D grayscale schematic of (<b>f</b>).</p>
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<p>Overall network of MBS-Net.</p>
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<p>U-Net structure diagrams of different depths in the background information estimation stage. (<b>a</b>) Network structure diagram of L1. (<b>b</b>) Network structure diagram of L2. (<b>c</b>) Network structure diagram of L4. (<b>d</b>) Network structure diagram of L8.</p>
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<p>U-Net structure diagrams of different depths in the background information estimation stage. (<b>a</b>) Network structure diagram of L1. (<b>b</b>) Network structure diagram of L2. (<b>c</b>) Network structure diagram of L4. (<b>d</b>) Network structure diagram of L8.</p>
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<p>(<b>a</b>,<b>b</b>) The structure of two types of multi-scale convolution block.</p>
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<p>The diagram of original image processing.</p>
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<p>Schematic diagram of local cloud background suppression results.</p>
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<p>Schematic diagram of global undulating background suppression results.</p>
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<p>(<b>a</b>) Original Image. (<b>a−1</b>) A 3D grayscale of (<b>a</b>). (<b>b</b>) Median filtering. (<b>b−1</b>) A 3D grayscale of (<b>b</b>). (<b>c</b>) Top-Hat. (<b>c−1</b>) A 3D grayscale of (<b>c</b>). (<b>d</b>) BM3D. (<b>d−1</b>) A 3D grayscale of (<b>d</b>). (<b>e</b>) DnCNN. (<b>e−1</b>) A 3D grayscale of (<b>e</b>). (<b>f</b>) Source-extractor. (<b>f−1</b>) A 3D grayscale of (<b>f</b>). (<b>g</b>) BSC-Net. (<b>g−1</b>) A 3D grayscale of (<b>g</b>). (<b>h</b>) MBS-Net. (<b>h−1</b>) A 3D grayscale of (<b>h</b>).</p>
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<p>Diagram of Loss and PSNR variation. (<b>a</b>) Schematic diagram of loss variation curve. (<b>b</b>) Schematic diagram of PSNR.</p>
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<p>Loss and PSNR variation diagram of different deep networks. (<b>a</b>) Schematic diagram of loss variation curve. (<b>b</b>) Schematic diagram of PSNR.</p>
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25 pages, 24987 KiB  
Article
Exploring the Potential of Solar-Induced Chlorophyll Fluorescence Monitoring Drought-Induced Net Primary Productivity Dynamics in the Huang-Huai-Hai Plain Based on the SIF/NPP Ratio
by Yanan Wang, Jingchi He, Ting Shao, Youjun Tu, Yuxin Gao and Junli Li
Remote Sens. 2023, 15(13), 3276; https://doi.org/10.3390/rs15133276 - 26 Jun 2023
Cited by 1 | Viewed by 1740
Abstract
Drought causes significant losses in vegetation net primary productivity (NPP). However, the lack of real-time, large-scale NPP data poses challenges in analyzing the relationship between drought and NPP. Solar-induced chlorophyll fluorescence (SIF) offers a real-time approach to monitoring drought-induced NPP dynamics. Using two [...] Read more.
Drought causes significant losses in vegetation net primary productivity (NPP). However, the lack of real-time, large-scale NPP data poses challenges in analyzing the relationship between drought and NPP. Solar-induced chlorophyll fluorescence (SIF) offers a real-time approach to monitoring drought-induced NPP dynamics. Using two drought events in the Huang–Huai–Hai Plain from 2010 to 2020 as examples, we propose a new SIF/NPP ratio index to quantify and evaluate SIF’s capability in monitoring drought-induced NPP dynamics. The findings reveal distinct seasonal changes in the SIF/NPP ratio across different drought events, intensities, and time scales. SIF demonstrates high sensitivity to commonly used vegetation greenness parameters for NPP estimation (R2 > 0.8, p < 0.01 for SIF vs NDVI and SIF vs LAI), as well as moderate sensitivity to land surface temperature (LST) and a fraction of absorbed photosynthetically active radiation (FAPAR) (R2 > 0.5, p < 0.01 for SIF vs FAPAR and R2 > 0.6, p < 0.01 for SIF vs LST). However, SIF shows limited sensitivity to precipitation (PRE). Our study suggests that SIF has potential for monitoring drought-induced NPP dynamics, offering a new approach for real-time monitoring and enhancing understanding of the drought–vegetation productivity relationship. Full article
(This article belongs to the Section Remote Sensing in Agriculture and Vegetation)
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<p>Location of the HHH Plain and land use types in the region.</p>
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<p>Flow chart of the research method.</p>
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<p>Spatial distribution of the GOSIF maximum (<b>a</b>), GLASS NPP maximum (<b>b</b>), GOSIF mean (<b>c</b>), GLASS NPP mean (<b>d</b>), GOSIF maximum (<b>e</b>), and GLASS NPP maximum (<b>f</b>) from 2010 to 2020.</p>
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<p>Results of the image-by-image correlation analysis of GOSIF and GLASS NPP in the HHH Plain from 2010 to 2020 (<b>a</b>) and significant values (<b>b</b>).</p>
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<p>Standardized GOSIF and GLASS NPP changes for the 8-day interval from 2010 to 2020.</p>
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<p>Results of the pixel-by-pixel correlation analysis between GOSIF and GLASS NPP (<b>a</b>–<b>d</b>) and significant values (<b>e</b>–<b>h</b>) from October 2013 to September 2014, May to December 2019, May to June 2020, and October to December 2020.</p>
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<p>Dynamic changes in SIF/NPP with 8-day time intervals from October 2013 to September 2014 (<b>a</b>) and May to December 2019 (<b>b</b>).</p>
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<p>Dynamic changes in SIF/NPP with an 8-day time interval in (<b>a</b>) mildly drought-affected regions, (<b>b</b>) moderately drought-affected regions, (<b>c</b>) severely drought-affected regions, and (<b>d</b>) extremely drought-affected regions from October 2013 to September 2014.</p>
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<p>Dynamic changes in SIF/NPP with an 8-day time interval in (<b>a</b>) mildly drought-affected regions, (<b>b</b>) moderately drought-affected regions, (<b>c</b>) severely drought-affected regions, and (<b>d</b>) extremely drought-affected regions from May to December 2019.</p>
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<p>Correlation between GOSIF and GLASS NPP during drought events of 40 (<b>a</b>), 80 (<b>b</b>), 120 (<b>c</b>), 160 (<b>d</b>), 200 (<b>e</b>), 240 (<b>f</b>), 280 (<b>g</b>), and 320 days (<b>h</b>) from October 2013 to September 2014.</p>
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<p>Correlation between GOSIF and GLASS NPP during drought events of 40 (<b>a</b>), 80 (<b>b</b>), 120 (<b>c</b>), 160 (<b>d</b>), and 200 days (<b>e</b>) from May to December 2019.</p>
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<p>Results of the correlation analysis between GOSIF and FAPAR (<b>a</b>), LAI (<b>b</b>), LST (<b>c</b>), NDVI (<b>d</b>), and rain (<b>e</b>) from October 2013 to September 2014, and between GOSIF and FAPAR (<b>f</b>), LAI (<b>g</b>), LST (<b>h</b>), NDVI (<b>i</b>), and PRE from May to December 2019 (<b>j</b>).</p>
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<p>Results of the correlation analysis between GOSIF and FAPAR lags of 16 (<b>a</b>), 32 (<b>b</b>), 48 (<b>c</b>), 64 (<b>d</b>), and 80 days (<b>e</b>) for the period October 2013 to September 2014.</p>
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<p>Results of the correlation analysis of GOSIF with LST lags of 8 (<b>a</b>), 24 (<b>b</b>), 40 (<b>c</b>), and 56 days (<b>d</b>) for the period October 2013 to September 2014.</p>
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<p>Results of the correlation analysis between SIF and FAPAR lags of 24 (<b>a</b>), 48 (<b>b</b>), 72 (<b>c</b>), 96 (<b>d</b>), and 112 days (<b>e</b>) for the period May to December 2019.</p>
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<p>Results of the correlation analysis between SIF and LST lags of 16 (<b>a</b>), 32 (<b>b</b>), 48 (<b>c</b>), and 64 days (<b>d</b>) for the period May to December 2019.</p>
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10 pages, 1011 KiB  
Article
Assessing the Relationship between LAMS and CT Perfusion Parameters in Acute Ischemic Stroke Secondary to Large Vessel Occlusion
by Karissa C Arthur, Shenwen Huang, Julie C. Gudenkauf, Alireza Mohseni, Richard Wang, Alperen Aslan, Mehreen Nabi, Meisam Hoseinyazdi, Brenda Johnson, Navangi Patel, Victor C Urrutia and Vivek Yedavalli
J. Clin. Med. 2023, 12(10), 3374; https://doi.org/10.3390/jcm12103374 - 9 May 2023
Cited by 4 | Viewed by 1894
Abstract
Background: The Los Angeles Motor Scale (LAMS) is a rapid pre-hospital scale used to predict stroke severity which has also been shown to accurately predict large vessel occlusions (LVOs). However, to date there is no study exploring whether LAMS correlates with the computed [...] Read more.
Background: The Los Angeles Motor Scale (LAMS) is a rapid pre-hospital scale used to predict stroke severity which has also been shown to accurately predict large vessel occlusions (LVOs). However, to date there is no study exploring whether LAMS correlates with the computed tomography perfusion (CTP) parameters in LVOs. Methods: Patients with LVO between September 2019 and October 2021 were retrospectively reviewed and included if the CTP data and admission neurologic exams were available. The LAMS was documented based on emergency personnel exams or scored retrospectively using an admission neurologic exam. The CTP data was processed by RAPID (IschemaView, Menlo Park, CA, USA) with an ischemic core volume (relative cerebral blood flow [rCBF] < 30%), time-to-maximum (Tmax) volume (Tmax > 6 s delay), hypoperfusion index (HI), and cerebral blood volume (CBV) index. Spearman’s correlations were performed between the LAMS and CTP parameters. Results: A total of 85 patients were included, of which there were 9 intracranial internal carotid artery (ICA), 53 proximal M1 branch middle cerebral artery M1, and 23 proximal M2 branch occlusions. Overall, 26 patients had LAMS 0–3, and 59 had LAMS 4–5. In total, LAMS positively correlated with CBF < 30% (Correlation Coefficient (CC): 0.32, p < 0.01), Tmax > 6 s (CC:0.23, p < 0.04), HI (CC:0.27, p < 0.01), and negatively correlated with the CBV index (CC:−0.24, p < 0.05). The relationships between LAMS and CBF were < 30% and the HI was more pronounced in M1 occlusions (CC:0.42, p < 0.01; 0.34, p < 0.01 respectively) and proximal M2 occlusions (CC:0.53, p < 0.01; 0.48, p < 0.03 respectively). The LAMS also correlated with a Tmax > 6 s in M1 occlusions (CC:0.42, p < 0.01), and negatively correlated with the CBV index in M2 occlusions (CC:−0.69, p < 0.01). There were no significant correlations between the LAMS and intracranial ICA occlusions. Conclusions: The results of our preliminary study indicate that the LAMS is positively correlated with the estimated ischemic core, perfusion deficit, and HI, and negatively correlated with the CBV index in patients with anterior circulation LVO, with stronger relationships in the M1 and M2 occlusions. This is the first study showing that the LAMS may be correlated with the collateral status and estimated ischemic core in patients with LVO. Full article
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<p>Flow chart of retrospective chart review to identify patients with LVO, admission neurologic exam, and perfusion data. LVO = large vessel occlusion; ICA = internal carotid artery; M1 = M1 branch of middle cerebral artery (MCA), M2 = M2 branch of MCA.</p>
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19 pages, 3544 KiB  
Article
Estimation of Quercus Biomass in Shangri-La Based on GEDI Spaceborne Lidar Data
by Li Xu, Qingtai Shu, Huyan Fu, Wenwu Zhou, Shaolong Luo, Yingqun Gao, Jinge Yu, Chaosheng Guo, Zhengdao Yang, Jinnan Xiao and Shuwei Wang
Forests 2023, 14(5), 876; https://doi.org/10.3390/f14050876 - 24 Apr 2023
Cited by 10 | Viewed by 2254
Abstract
Accurately estimating forest biomass based on spaceborne lidar on a county scale is challenging due to the incomplete coverage of spaceborne lidar data. Therefore, this research aims to interpolate GEDI spots and explore the feasibility of approaches to improving Quercus forest biomass estimation [...] Read more.
Accurately estimating forest biomass based on spaceborne lidar on a county scale is challenging due to the incomplete coverage of spaceborne lidar data. Therefore, this research aims to interpolate GEDI spots and explore the feasibility of approaches to improving Quercus forest biomass estimation accuracy in the alpine mountains of Yunnan Province, China. This paper uses GEDI data as the main information source and a typical mountainous area in Shangri-La, northwestern Yunnan Province, China, as the study area. Based on the pre-processing of light spots. A total of 38 parameters were extracted from the canopy and vertical profiles of 1307 light spots in the study area, and the polygon data of the whole study area were obtained from the light spot data through Kriging interpolation. Multiple linear regression, support vector regression, and random forest were used to establish biomass models. The results showed that the optimal model is selected using the semi-variance function for the Kriging interpolation of each parameter of GEDI spot, the optimal model of modis_nonvegetated is a linear model, and the optimal model for rv, sensitivity, and modis_treecover is the exponential model. Analysis of the correlation between 39 parameters extracted from GEDI L2B and three topographic factors with oak biomass showed that sensitivity had a highly significant positive correlation (p < 0.01) with Quercus biomass, followed by a significant negative correlation (p < 0.05) with aspect and modis_nonvegation. After variable selection, the estimation model of Quercus biomass established using random forest had R2 = 0.91, RMSE = 19.76 t/hm2, and the estimation accuracy was better than that of multiple linear regression and support vector regression. The estimated total biomass of Quercus in the study area was mainly distributed between 26.48 and 257.63 t/hm2, with an average value of 114.33 t/hm2 and a total biomass of about 1.26 × 107 t/hm2. This study obtained spatial consecutive information using Kriging interpolation. It provided a new research direction for estimating other forest structural parameters using GEDI data. Full article
(This article belongs to the Special Issue Forestry Remote Sensing: Biomass, Changes and Ecology)
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<p>(<b>a</b>) is the location of Shangri-La in Yunnan Province; (<b>b</b>) is the distribution of Quercus and sample sites in Shangri-La.</p>
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<p>GEDI ground sampling mode.</p>
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<p>(<b>a</b>) Distribution of all light spots. (<b>b</b>) Distribution of light spots after filtering.</p>
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<p>Technology roadmap.</p>
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<p>Matrix of correlation coefficients between GEDI variables and Quercus biomass.</p>
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<p>Scatterplot of measured biomass: (<b>a</b>) is the multiple linear regression; (<b>b</b>) is the support victor machine; (<b>c</b>) is the random forest.</p>
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<p>Biomass distribution map of Quercus in Shangri-La.</p>
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13 pages, 3454 KiB  
Article
Evaluation of a Cardiovascular Systems Model for Design and Analysis of Hemodynamic Safety Studies
by Yu Fu, Nelleke Snelder, Tingjie Guo, Piet H. van der Graaf and Johan. G. C. van Hasselt
Pharmaceutics 2023, 15(4), 1175; https://doi.org/10.3390/pharmaceutics15041175 - 7 Apr 2023
Viewed by 1486
Abstract
Early prediction, quantification and translation of cardiovascular hemodynamic drug effects is essential in pre-clinical drug development. In this study, a novel hemodynamic cardiovascular systems (CVS) model was developed to support these goals. The model consisted of distinct system- and drug-specific parameter, and uses [...] Read more.
Early prediction, quantification and translation of cardiovascular hemodynamic drug effects is essential in pre-clinical drug development. In this study, a novel hemodynamic cardiovascular systems (CVS) model was developed to support these goals. The model consisted of distinct system- and drug-specific parameter, and uses data for heart rate (HR), cardiac output (CO), and mean atrial pressure (MAP) to infer drug mode-of-action (MoA). To support further application of this model in drug development, we conducted a systematic analysis of the estimation performance of the CVS model to infer drug- and system-specific parameters. Specifically, we focused on the impact on model estimation performance when considering differences in available readouts and the impact of study design choices. To this end, a practical identifiability analysis was performed, evaluating model estimation performance for different combinations of hemodynamic endpoints, drug effect sizes, and study design characteristics. The practical identifiability analysis showed that MoA of drug effect could be identified for different drug effect magnitudes and both system- and drug-specific parameters can be estimated precisely with minimal bias. Study designs which exclude measurement of CO or use a reduced measurement duration still allow the identification and quantification of MoA with acceptable performance. In conclusion, the CVS model can be used to support the design and inference of MoA in pre-clinical CVS experiments, with a future potential for applying the uniquely identifiable systems parameters to support inter-species scaling. Full article
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<p>Model structure of the CVS model consisting of five hemodynamic variables of HR, SV, TPR, CO, and MAP and a one-compartment pharmacokinetic model of the hypothetical drug [<a href="#B7-pharmaceutics-15-01175" class="html-bibr">7</a>]. CO is defined as the product of HR and SV, while MAP is the product of CO and TPR. The drug affects the production rate of HR, SV, or TPR. C: drug concentration (ng/mL); HR: heart rate (beats/min); SV: stroke volume (mL/beat); TPR: total peripheral resistance (mmHg∙min/mL); CO: cardiac output (mL/min); MAP: mean arterial pressure (mmHg); FB: feedback effect of MAP (mmHg<sup>−1</sup>); E<sub>drug</sub>: drug effect on three primary effect sites. K<sub>in</sub>: production rate constant (K<sub>in_HR</sub>: beats*h<sup>−1</sup>/min, K<sub>in_SV</sub>: mL*h<sup>−1</sup>/beat, K<sub>in_TPR</sub>: mmHg*min*h<sup>−1</sup>/mL); K<sub>out</sub>: dissipation rate constant (h<sup>−1</sup>); k: elimination rate constant of the hypothetical drug (h<sup>−1</sup>).</p>
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<p>Overview identifiability analyses. SSE: stochastic simulation and re-estimation; PsN: Perl-speaks-NONMEM toolkit; HR: heart rate; SV: stroke volume; TPR: total peripheral resistance; MoA: mode-of-action; OFV: objective function value.</p>
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<p>Identifiability of drug- and system-specific parameters. HR: heart rate; CO: cardiac output; SV: stroke volume; TPR: total peripheral resistance; MAP: mean arterial pressure. Relative prediction errors after simulation and re-estimation (SSE) analysis using observations for HR and MAP (<b>top</b>) or observations of HR, CO, and MAP (<b>bottom</b>) following three ascending doses. EC<sub>50</sub>: the concentration at which half of maximum effect is achieved; FB: regulatory feedback effect from MAP to HR, SV, and TPR; HR<sub>0</sub>: baseline value of HR; MAP<sub>0</sub>: baseline value of MAP; CO<sub>0</sub>: baseline value of CO; Kout<sub>HR</sub>: dissipation rate of HR; Kout<sub>SV</sub>: dissipation rate of SV; Kout<sub>TPR</sub>: dissipation rate of TPR; HR<sub>SV</sub>: direct effect constant between HR and SV; Hor<sub>HR</sub>: horizontal displacement of circadian rhythm of HR; Amp<sub>HR</sub>: amplitude of circadian rhythm of HR; Hor<sub>TPR</sub>: horizontal displacement of circadian rhythm of TPR.</p>
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<p>Impact of duration of experimental observations on the percentage of runs with correct identification of mechanisms of action. Results from simulation and re-estimation analyses using either observations of HR and MAP or observations of HR, CO, and MAP within 3 h, 6 h, 12 h, and 24 h. Emax was fixed as −1 and EC<sub>50</sub> was fixed as 100 ug/mL in the original model. Emax was fixed to −1 and EC<sub>50</sub> was fixed to 100 ug/mL in the original model. Correct identification is based on applying a likelihood ratio test compared to the base (no drug) model.</p>
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<p>Impact of duration of experimental observations on relative prediction error of drug effect estimate EC<sub>50</sub>. Results from simulation and re-estimation analyses using either observations of HR and MAP or observations of HR, CO, and MAP within 3 h, 6 h, 12 h, and 24 h, while Emax was fixed as −1 and EC<sub>50</sub> was fixed as 100 ug/mL in the original model.</p>
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<p>Comparison of magnitudes of circadian rhythm on HR or TPR and magnitudes of drug effect. Comparison of EC<sub>50</sub> as 100 ng/mL (<b>left</b>), 1000 ng/mL (<b>middle</b>), and 100 ug/mL (<b>right</b>). Dark blue solid line: drug effect following a dose of 0.1 mg/kg; orange solid line: drug effect following a dose of 1 mg/kg; green solid line: drug effect following a dose of 10 mg/kg; black dashed line: magnitude of circadian rhythm effect of HR; gray dashed line: circadian rhythm effect of TPR.</p>
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<p>Impact of number of animals used in experiments on percentage of runs with correct identification of mechanism of action. Derived using SSE analyses using data for 3, 4, or 5 animals with observations of HR and MAP or observations of HR, CO, and MAP, while Emax was fixed as −1 and EC<sub>50</sub> was fixed as 100 ug/mL in original model. Correct identification is based on applying a likelihood ratio test compared to the base (no drug) model.</p>
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<p>Impact of number of animals used in experiments on relative prediction error of drug effect estimate EC<sub>50</sub>. Derived using SSE analyses using data for 3, 4, or 5 animals with observations of HR and MAP or observations of HR, CO, and MAP, while Emax was fixed as −1 and EC<sub>50</sub> was fixed as 100 ug/mL in the original model.</p>
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