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Journal of Arid Land  2023, Vol. 15 Issue (6): 710-723    DOI: 10.1007/s40333-023-0103-7
Research article     
Modelling the dead fuel moisture content in a grassland of Ergun City, China
CHANG Chang1,2, CHANG Yu1,*(), GUO Meng3, HU Yuanman1,4
1CAS Key Laboratory of Forest Ecology and Management, Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, China
2University of Chinese Academy of Sciences, Beijing 100049, China
3School of Geographical Sciences, Northeast Normal University, Changchun 130024, China
4E'erguna Wetland Ecosystem National Research Station, Hulunbuir 022250, China
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Abstract  

The dead fuel moisture content (DFMC) is the key driver leading to fire occurrence. Accurately estimating the DFMC could help identify locations facing fire risks, prioritise areas for fire monitoring, and facilitate timely deployment of fire-suppression resources. In this study, the DFMC and environmental variables, including air temperature, relative humidity, wind speed, solar radiation, rainfall, atmospheric pressure, soil temperature, and soil humidity, were simultaneously measured in a grassland of Ergun City, Inner Mongolia Autonomous Region of China in 2021. We chose three regression models, i.e., random forest (RF) model, extreme gradient boosting (XGB) model, and boosted regression tree (BRT) model, to model the seasonal DFMC according to the data collected. To ensure accuracy, we added time-lag variables of 3 d to the models. The results showed that the RF model had the best fitting effect with an R2 value of 0.847 and a prediction accuracy with a mean absolute error score of 4.764% among the three models. The accuracies of the models in spring and autumn were higher than those in the other two seasons. In addition, different seasons had different key influencing factors, and the degree of influence of these factors on the DFMC changed with time lags. Moreover, time-lag variables within 44 h clearly improved the fitting effect and prediction accuracy, indicating that environmental conditions within approximately 48 h greatly influence the DFMC. This study highlights the importance of considering 48 h time-lagged variables when predicting the DFMC of grassland fuels and mapping grassland fire risks based on the DFMC to help locate high-priority areas for grassland fire monitoring and prevention.



Key wordsdead fuel moisture content (DFMC)      random forest (RF) model      extreme gradient boosting (XGB) model      boosted regression tree (BRT) model      grassland      Ergun City     
Received: 21 October 2022      Published: 30 June 2023
Corresponding Authors: * CHANG Yu (E-mail: changyu@iae.ac.cn)
Cite this article:

CHANG Chang, CHANG Yu, GUO Meng, HU Yuanman. Modelling the dead fuel moisture content in a grassland of Ergun City, China. Journal of Arid Land, 2023, 15(6): 710-723.

URL:

http://jal.xjegi.com/10.1007/s40333-023-0103-7     OR     http://jal.xjegi.com/Y2023/V15/I6/710

Fig. 1 Land cover types of Ergun City (a) and an overview of fuel moisture content meters (b). The land cover type data are derived from https://www.resdc.cn/Default.aspx.
Fig. 2 Fuel moisture content meter and its components. The anemometer is placed 1 m above the ground.
Season Range of date Temperature (T) threshold
Spring 15 May 2021-29 June 2021 10°C≤T<22°C
Summer 30 June 2021-31 July 2021 T≥22°C
Autumn 1 August 2021-9 October 2021 10°C≤T<22°C
Winter (apart from midwinter) 9 April 2021-14 May 2021 and 10 October 2021-7 November 2021 T<10°C
Table 1 Seasonal division of this study according to the average daily temperature
Fig. 3 Box plot of the seasonal differences in the dead fuel moisture content (DFMC). The upper and lower limits of the box indicate the 75th and 25th percentile values, respectively; the horizontal lines and small squares in each box represent the medians and means, respectively; the upper and lower whiskers show the maximum and minimum values, respectively; and the scattered points above the maximum values are outliers.
Fig. 4 Performances of the boosted regression tree (BRT) model (a), extreme gradient boosting (XGB) model (b), and random forest (RF) model (c) in predicting the DFMC. MAE is the mean absolute error.
Fig. 5 Performance of the BRT, XGB, and RF models in spring (a1, b1, and c1), summer (a2, b2, and c2), autumn (a3, b3, and c3), and winter (a4, b4, and c4)
Fig. 6 Variable importance changes with time lags in the RF model in spring (a), summer (b), autumn (c), winter (d), and the all year (e). IncNodePurity is the degree of importance. The negative values of the x-axis represent the hours before the time of measurement.
Fig. 7 Prediction performance along with the time-lag data 72 h before the time of measuring. (a), R2; (b), MAE.
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