Allometric equations coupled with remotely sensed variables to estimate carbon stocks in date palms
Introduction
Some palm species are considered keystone and provide multiple ecosystem services, such as CS (Van der Hoek, Solas and Peñuela, 2019). The amount of carbon that can be sequestered in palms is relatively high compared to some other plant species. In their study of the relationship between land use and CS in northeastern Brazil, Sanquetta et al., 2015 found that land planted with palms provided 40 t C ha−1 while lands used for pasture and agriculture provided only 8 t C ha−1 and 5 t C ha−1, respectively. In another study in Northeast India, Singh et al. (2018) recorded considerably higher amounts of carbon in oil palm plantations than in shifting cultivation fallows. They concluded that a 10 years old oil palm plantation could sequester up to 3.7 t C ha−1 year−1. Hence, palms generate economic benefit and contribute to carbon storage in more sustainable ways especially when planted in areas of low productivity or on degraded lands.
Afforestation projects can be used to earn carbon credits and reduce the carbon footprint. This type of supportive efforts has a growing interest among policymakers and governments (Baral and Guha, 2004; Lal, 2003, 2004). Therefore, estimation of CS in forests and plantations is an important measure towards assessing mitigation effects on global change (Ebuy et al., 2011). Many destructive techniques (felling or harvesting) exist to directly estimate CS (Gibbs et al., 2007). Although these techniques provide the most accurate measure of biomass, they ultimately rely on ground measurement and can cause severe destruction to the forests as well as a risk of environmental deterioration (Khalid and Hamid, 2017; Maulana et al., 2016). In addition, such methods are tedious and time consuming (Ebuy et al., 2011), hence they cannot be used routinely. Therefore, developing biomass equations (allometry) that rely on non-destructive measurements, is very essential in estimating biomass. Subsequently, allometric equations have been developed and used to estimate tree biomass and CS from dendrometric measures, such as tree diameters and height (Ebuy et al., 2011; Picard et al., 2012). Notwithstanding, the number of trees destructively sampled to build allometric equations is not constant and differs from one study to another. Currently, there is no consensus on that number, as this is often dependent on resource availability and permission to harvest trees (Yuen et al., 2016). For example, Russell (1983) and Deans et al., 1996 used 15 and 14 trees, while Brown et al. (1995) and Khalid, Zin, & Anderson, (1999a) used only 8 and 10 trees, respectively to build their allometric equations.
Different quantitative variables were considered when building oil palm biomass allometric equations (Korom et al., 2016) (Appendix I). Hensen and Chang (2003) used age as a predictor to estimate the standing biomass of oil palm in tons per hectare. Others used structural variables such as total height (H) and Ht (Dewi et al., 2009; Khalid et al., 1999a; Thenkabail et al., 2004), while Corley and Tinker (2008) Corley et al. (1971) used diameter at breast height, number of fronds, leaf area, rachis and petiole length, rachis and petiole cross-sectional area at intervals, and volume of petiole sections in their pioneer study to estimate the average yield of oil palms. More recently, allometric equations have been used, coupled with RS and field-based structural variables measurements (Fonton et al., 2017; Issa et al., 2019; Dahy et al., 2019). Furthermore, Cheng et al. (2014)recommended to develop more equations with different field structural variables that can be linked to RS predictors. Likewise, Jucker et al. (2017) suggested in their review of allometric equations to develop a new generation of allometric equations that estimate biomass based on attributes which can be remotely sensed.
Most biomass equations, whether species-specific or multi-species, have been developed for tropical rainforest ecosystems because of their relevance to the global carbon cycle (Basuki et al., 2009; S. Brown, 1997; Chave et al., 2005; Cole and Ewel, 2006; Makinde et al., 2017). A few plant species biomass assessment equations are available for desert ecosystems (Chao and Krueger, 2007). Nonetheless, none of these were used to fit one of the most important fruit crops in the arid regions, Phoenix dactylifera, date palm.
According to Food and Agriculture Statistics Database (FAOSTAT, 2003) and reported in Abd Rabou (2017), the world's total number of date palms is about 120 million, distributed throughout 30 countries and producing nearly 7.5 million tons of fruit per year. Over two-third of this amount are produced in the Arab World (El-Juhany, 2010). Three of the top 10 date producers worldwide are in the Arabian Peninsula, namely: Saudi Arabia, United Arab Emirates (UAE), and Oman (Kader and Hussein, 2009; AOAD, 2008). The UAE has the largest number of date palms for any single country in the world. In 2008, the UAE had more than 16 million date palms producing around three quarters of a million tons of dates (El-Juhany, 2010). By the year 2020, the estimated number of date palms in the UAE has reached 40 million, as reported by the UAE University (UAEU) – based, Date Palms Research and Development Unit (UAEU, 2020). Furthermore, the UAE possesses at least 200 cultivars, 68 of which are the most important commercially (Jaradat and Zaid, 2004).
Date palms possess multipurpose advantages, including environmental benefits, especially for the Arabian Peninsula nations, such as the UAE, where date palms have been an integral part of the farming system. More than 90% of the UAE territory is covered by desert ecosystems representing more than two-thirds of the country's land area. Date palm species are a good alternative for CS in such arid ecosystems as they require minimum water supply and tolerate harsh growth conditions: high temperatures, drought and high levels of salinity. In fact, it is the most salt tolerant plant of all fruit crops (Alhammadi and Kurup, 2012; El-Juhany, 2010; Zohary and Hopf, 2000). To estimate date palms biomass and its carbon content, it is necessary to quantify the biomass in all palm components. Moreover, it would be more accurate to include both the aboveground and belowground biomass in estimating the CS, as both are available for recycling in the ecosystem at replanting (Khalid, Zin and Anderson, 1999b).
The objectives of the present study are: (1) to identify most relevant structural field variables for the estimation of date palms biomass; (2) to develop specific allometric biomass equations integrable with RS; (3) to estimate CS in date palms; and (4) to assess the potential of date palm species to improve soil CS in such desert ecosystems.
Section snippets
Study area
The study area encompasses the whole emirate of Abu Dhabi, UAE. Yet, the fieldwork was conducted inside three farms located near Al-Ain city, UAE in the western part of the Arabian Peninsula and located at 24° 12′ 27″ N and 55° 44′ 40″ E. Al-Ain city was established around an old date palms oasis and as the city expanded, the date palms plantations expanded as well. The estimated number of date palms in Al-Ain area is about 8.5 million palms representing more than 20% of the total date palms
Field variables, date palms’ components and age
The correlation coefficients between fresh and dry weight for the palm's crown trunk and root components were estimated at 0.99, 0.97 and 0.97, respectively; while the correlation between the total fresh weight and the total dry weight gave a value of 0.99. Furthermore, the dry to fresh weight ratio (dry to fresh factor (DF)), for the belowground biomass was estimated at 0.45, while that of the aboveground biomass was calculated at 0.40 (Table 4). As for the non-structural variables, age proved
Discussion
The correlation coefficient between the total fresh and dry weights of date palm was 0.99, in agreement with values usually recorded in palm experiments (Corley et al., 1971). Some authors used fresh weight to build their allometric equations, as it was the case in some southern Asia oil palms studies (Dewi et al., 2009; H. Khalid et al., 1999a). Others used dry weight as in some tropical and west African regions (Corley et al., 1971; Thenkabail et al., 2004) (Appendix I). In this study, we
Conclusions & recommendations
A key objective of this study was to develop specific allometric biomass equations for assessing carbon sequestration in date palms of the UAE and to estimate the potential of date palm species to improve soil carbon sequestration in such desert ecosystems. Allometric equations using structural variables that could be linked to RS observations were developed for date palms at different age stages. Based on field and lab works, CA was found to best estimate CB and SOC, while Ht was the best
Credit author statement
Salem Issa presented idea and verified the analytical idea and supervised the findings of this work. Basam Dahy conducted the experiments and performed the computations. Taoufik Ksiksi helped supervise the project. Nazmi Saleous contributed to the final version of the manuscript. All authors discussed the results and contributed to the final manuscript.
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
We would like to express our appreciation to the Research Affairs - United Arab Emirates University for their financial support under fund Grand # 31S247. We would also like to express sincere gratitude to Dr. Mohamed T. Moussa for his assistance in the UAEU ecology Lab and to Al Foah farm company for providing us free access to their premises and to allow us to use their equipment and their support with logistic assistance.
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