فصلنامه علمی- پژوهشی اطلاعات جغرافیایی « سپهر»

فصلنامه علمی- پژوهشی اطلاعات جغرافیایی « سپهر»

کاربرد سنجش از دور در مدل‌سازی اثرهای فاصله از جاده بر تجمع فلزات سنگین در برگ و خاک گونه بلوط ایرانی - مطالعه موردی: جنگل کاکارضا خرم‌آباد، لرستان

نوع مقاله : مقاله پژوهشی

نویسندگان
1 پژوهشگر مقطع پسا دکتری جنگلداری، دانشکده منابع طبیعی، دانشگاه علوم کشاورزی منابع طبیعی ساری، مازندران، ساری، ایران
2 استاد گروه جنگلداری، دانشکده منابع طبیعی، دانشگاه علوم کشاورزی و منابع طبیعی ساری، ساری، ایران
3 دانشجوی دکتری جنگلداری، دانشکده منابع طبیعی، دانشگاه علوم کشاورزی و منابع طبیعی ساری، ایران
4 دانشیار گروه جنگلداری، دانشکده منابع طبیعی، دانشگاه علوم کشاورزی و منابع طبیعی ساری، ساری، ایران
چکیده
آلودگی فلزات سنگین چالش بزرگی برای محیط زیست است. با افزایش سطح آلودگی، روش‌های پایش سنتی نمی‌توانند به سرعت اطلاعاتی در مورد آلودگی مناطق بزرگ به دست دهند. با توجه به پرهزینه و زمان‌بر بودن روش‌های آزمایشگاهی استفاده از تصاویر ماهواره‌ای و روش‌های سنجش از دور با در نظر گرفتن دقت کافی می‌توانند مکمل مناسبی در این زمینه باشند.
پژوهش حاضر با هدف بررسی آلودگی فلزات سنگین سرب، روی و مس در خاک و برگ جنگل‌های بلوط ایرانی واقع در جنگل کاکارضا، استان لرستان با بکارگیری فن‌آوری سنجش از دور و تصاویر ماهواره Sentinel-2 به کمک شاخص‌های آلودگی (NDVI، HMSSI، SAVI و PSRI) انجام شد.
نتایج پژوهش نشان داد که غلظت فلزات سنگین در خاک با افزایش فاصله از جاده کاهش می یابد. بین مواد آلی و مس خاک در سطح پنج درصد همبستگی منفی معنی‌داری وجود دارد. مقادیر غلظت فلزات سنگین در برگ درختان بلوط ایرانی از مقادیر استاندارد جهانی کمتر است. در بخش نتایج شاخص تجمع زیستی نیز میزان فاکتور تجمع زیستی به ترتیب برای سرب، روی و مس (0.0،5.2 ،0.2) میلی‌‌گرم برکیلوگرم حاصل شد. در مقایسه پنج الگوریتم ناپارامتریک GAM، ANN، RF، SVM و KNN ، مدل (ANN) به ترتیب برای سه فلز Pb، Zn و Cu بالاترین مقادیر ضریب تبیین (0.85، 0.88 و 0.97) به دست آمد. به طور کلی نتایج نشان داد تصاویر Sentinel-2 به همراه مدل شبکه عصبی مصنوعی قابلیت خوبی در مدل‌سازی میزان شاخص تجمع زیستی دارند.
کلیدواژه‌ها

موضوعات


عنوان مقاله English

The application of remote sensing inmodeling the effects of distance from the road on the accumulation of heavy metals in leaves and soil of quercus branti species - Case study: Kakareza Forest, Khorramabad, Lorestan

نویسندگان English

Nastaran Nazariani 1
Asghar Fallah 2
Hava Hasanvand 3
Hassan Akbari 4
1 Postdoctoral Researcher in Forestry, Faculty of Natural Resources, Sari University of Agricultural Sciences, Mazandaran, Sari, Iran
2 Professor, Department of forestry, Faculty of natural resources, Sari University of agricultural sciences and natural resources ,Sari, Iran
3 PhD student in forestry, Faculty of natural resources, Sari University of agricultural sciences and natural resources, Sari, Iran.
4 Associate Professor department of forestry,Faculty of natural resources, Sari University of agricultural sciences and natural resources, Sari, Iran
چکیده English

Extended Abstract
Introduction
The traditional method of chemical analysis has high accuracy and precision. However, it is time-consuming and laborious, and it is not possible to obtain continuous information about the pollutant status over a large area. Therefore, there is an urgent need for a reliable and environmentally friendly method to quickly identify and investigate the distribution of heavy metals in soil and thus identify suspected contaminated areas (Scheuber & Köhl, 2003:33). Remote sensing is one of the ways that can provide a cost-effective and quick solution to investigate the distribution of heavy metals on a large scale using spectroscopic techniques (Bi et al., 2009:16). Habibi et al. (2023:4) also measured and evaluated the concentration of heavy metals in the aerial parts and soil of the tree species of Bandar Abbas city and also identified the species that has the highest potential for absorbing heavy metals. The results showed that the pattern of heavy metals in soil and leaves of tree species was Mn>Zn>Pb>Cd. (Nikolaevich, 2023:30) they addressed the modeling of heavy metal pollution in Central Russia based on satellite images and machine learning. Al, Fe, and Sb contamination were predicted for 3000 and 12100 grid nodes in an area of 500 km2 for the Central Russian region for 2019 and 2020. Estimating the amount of this pollution requires time and high cost. Considering the traffic on the Aleshtar -Khorramabad highway near Kakareza forests and the effect of heavy metal concentration in the soil and leaves of the oak species which can be caused by natural and human pollution, the accumulation of heavy metals in the species Iranian oak is a serious threat to this forest. Therefore, it is necessary to study and discuss pollutants and their effects on the environmental cycle. In this regard, considering the cost and time-consuming nature of traditional methods and since remote sensing methods are a suitable complement to traditional methods; the aim of the present research is to use remote sensing techniques and spectral analyses to evaluate and model the accumulation of heavy metals in Iranian oak species.
Materials and Methods
The present study is located on the road of Aleshtar -Khorramabad, 20 kilometers northwest of Khorramabad. For this purpose, five transects were created at distances adjacent to the road, 500 and 1000 meters on both sides of the road, and 10 x 10 m sample pieces were planted. Inside the sample plots, 30 soil samples were randomly collected and 30 leaf samples were collected from trees in all directions of the crown. To extract heavy metals from soil samples and plant samples, the acid digestion method was used and the physical characteristics of the soil were measured using standard methods. After preparing the samples, the concentration of Pb, Cu, and zinc heavy metals in soil and leaves was measured and the index of biological concentration of heavy metals from soil to leaves was calculated. Then the relationship between the concentration of heavy elements measured and the reflectance in different bands or band ratios at the corresponding sampling points was obtained. Non-parametric methods and generalized multiple linear regression models were used in order to model quantitative variables and spectral values corresponding to sample parts in satellite data. ArcGIS software was used to implement sample parts on the image, ENVI software was used for image processing, and STATISTICA software was used for modeling.
Results and Discussion
Cu and Pb in Iranian oak leaves had significant differences at different distances at the 0.05 level, but Cu did not have significant differences at different distances at the 0.05 level. Cu and Pb did not have significant differences in different soil intervals at the 0.05 level, but Cu had significant differences in different soil intervals at the 0.05 level. The bioconcentration factor was obtained as (0.2, 0.5, 0.2) mg/kg. The study of modeling of non-parametric methods using Sentinel-2 satellite data showed that the highest explanatory coefficient values (0.85, 0.88, and 0.97) were obtained for the three metals Cu, Pb, and Cu, respectively. The artificial neural network (ANN) algorithm obtained the highest accuracy. Also, according to the results of the random forest algorithm, for the three mentioned metals, PSRI, HMSSI, and PSRI indices are the most important in modeling.
Based on the findings, the concentration values of Cu and zinc were significantly different at different distances, but the Cu values were not significantly different at different distances. In this regard, Mansour concluded in 2014 that there is a significant difference between the concentration of Cu and zinc in the leaves of the species, which can be attributed to traffic density and human activities, and the high amount of zinc metal in this study is the wear of car tires؛ and stated that the concentration of Cu is caused by the production of greenhouse gases and the use of vehicles using Cu gasoline. Based on the findings, the values of Cu and zinc concentrations at different distances did not have significant differences, but the Cu values had significant differences at different distances. Sources of input of Cu element to the soil are urban, industrial, and agricultural waste, fertilizers, and chemicals that add it to the soil through liquid, solid, or mineral fertilizers. These findings are with the results of some researchers including Wu and colleagues (2010:38), Botsou et al. (2016:17) are consistent. Based on the findings obtained from the calculation of the bioconcentration index and their comparison with the classification proposed by Ma et al. (2001:25) for Iranian oak species plants in relation to Cu, zinc, and Cu metals from soil to leaves, it acts as an accumulating plant. In accordance with the results of this research, in the study of Khodakarmi et al. (2009:15), Iranian oak was included in the category of superabsorbent plants in relation to the accumulation of Cu pollutants, which has a high capacity in terms of root absorption. Also, Madejón et al. (2006:25) stated that oak leaves are more resistant than olive leaves. The concentrations of elements in leaves and fruits decrease with time and the risk of toxicity in the food web is reduced. The review and comparison of five algorithms showed that (ANN) the highest explanatory coefficient values (0.85, 0.88, and 0.97) were obtained for three metals, Cu, Zn, and Cu, respectively. Considering the importance of the PSRI synthetic band in increasing the accuracy of modeling with satellite images and the influence of the visible and near-infrared bands, the amount of reflection measured by the spectroscopic method showed that with the increase in the concentration of heavy elements, the amount of reflection in the visible and infrared range decreases (Liu et al., 2011:24).
Conclusion
The results showed that Sentinel-2 images along with artificial intelligence techniques have a relatively good ability to model the level of biological pollution index in the region. In line with the obtained results, it is suggested that the Iranian oak species is used to reduce pollution on highways because it accumulates heavy metals.

کلیدواژه‌ها English

Bio indicator
Leave
Modeling
Nonparametric methods
Quercus branti
Sentinel-2
Soil
Traffic
1- انصاری، راهنورد، سوادکوهی؛ امیر، آپتین، فرزاد. (1400). برآورد غلظت فلزات سنگین سرب و کادمیوم در خاک منطقه لنجان با استفاده از اندازه‌گیری زمینی و تصاویر ماهواره‌ای. مطالعات علوم محیط زیست، 6(1): 3459-3465.‎
2- پیری صحراگرد، زارع چاهوکی؛ حسین، محمدعلی. (1400). پیش‌بینی پراکنش رویشگاه بالقوه گونه Artemisia sieberi Besser با استفاده از روش‌‌های داده‌محور در مراتع پشتکوه استان یزد. حفاظت زیست‌بوم گیاهان، 9 (19):279-261.
3- جمینی، ذولفقاری، نصرآبادی، قبادی؛ داود،  امیرعلی، زهرا، شادی. (1395). چالش‌های زیست‌محیطی و اثرات آن بر ساکنین روستای بدرآباد با استفاده از روش نظریه بنیانی. جغرافیا و پایداری محیط، 6(2): 87-71.
4- حاج رسولی‌ها، امینی، هودجی، نجفی؛ شاپور، حسین، مهران، پیام. (1385). زیست‌ردیابی آلودگی هوا و خاک در منطقه اصفهان. پژوهش در علوم کشاورزی، 2(2): 54-39.
5- حبیبی، بهروزی، نوحه‌گر؛ سمانه، محمود، احمد. (1401). اندازه‌گیری و ارزیابی تجمع آلودگی فلزات سنگین در خاک و برگ سه‌ گونه‌ی درختی (چریش، کهور و کنوکارپوس) در شهر بندرعباس. فصلنامه علوم محیطی، انتشار آنلاین از 1 آبان 1401.
6- حسنوند، قاسمی آقباش، سلگی، پژوهان؛ هوا، فرهاد، عیسی، ایمان. (1397). اثرهای فاصله از جاده بر تجمع فلزات سنگین در خاک و برگ بلوط ایرانی (Quercus brantii) در بزرگراه الشتر - خرم‌آباد. پژوهش و توسعه جنگل، 4(1): 41-29.
7- حسینی، سبحان‌اردکانی، چراغی، لرستانی،  مریخ‌پور؛ نیره‌سادات، سهیل، مهرداد، بهاره، هاجر. (1399). امکان‌سنجی استفاده از بومادران (Achillea wilhelmsii) و ازمک (Cardaria draba) برای پایش و پالایش زیستی فلزات سنگین روی، سرب و نیکل در محیط کنار جاده‌ای. سلامت و محیط زیست، 13 (4) :620-607.
8- خداکرمی، شیروانی، زاهد امیری، متینی‌زاده، صفری؛ یحیی، انوشیروان، قوام‌الدین، محمد، هوشمند. (1389). مقایسة مقدار جذب فلز سرب در اندام‌های مختلف (ریشه، ساقه و برگ) نهال‌های یکسالة دو گونة بلوط ایرانی (Quercus brantii) و بنه (Pistacia atlantica) به روش محلول پاشی .مجله جنگل ایران، 1(4): 320-313.
9- طالبی، ثاقب طالبی، جهان‌بازی گوجانی؛ محمود، خسرو، حسن. (1385). بررسی نیاز رویشگاهی و برخی خصوصیات کمّی و کیفی بلوط ایرانی در جنگل‌های استان چهار محال و بختیاری. فصلنامة علمی -پژوهشی تحقیقات جنگل و صنوبر ایران، 14 (1): 79-67.
10- کشاورزشکری؛ عباس (1383). بررسی تأثیر اسیدیته خاک بر روی قابلیت دسترسی مواد مغذی N,P,K فلزات سنگین در روند رشد توده های دست کاشت توسکای ییلاقی، افرا پلت و کاج تدا در جنگل سیاهکل شمال ایران. رساله دکتری رشته علوم محیط زیست، دانشگاه آزاد اسلامی واحد علوم و تحقیقات تهران، صفحات1-128.
11- مجد، تائبی، افیونی؛ سعید، امیر، مجید. (1386). آلودگی خاک حاشیة خیابان‌های شهری به سرب و کادمیوم. محیط شناسی، 43(33): 10-1.
12- نظریانی، فلاح، حمیدی، ورامش؛ نسترن، اصغر،  سیدکوثر، سعید. (1401). برآورد مشخصه‌های کمّی جنگل‌های زاگرس با استفاده از الگوریتم‌های ناپارامتریک داده‌کاوی (بررسی موردی: کوهدشت، لرستان). پژوهش و توسعه جنگل، 8 (3): 263-249.
 
13- Ahmed, F., Dwivedi, S., Shaalan, N. M., Kumar, S., Arshi, N., Alshoaibi, A., & Husain, F. M. (2020). Development of selenium nanoparticle based agriculture sensor for heavy metal toxicity detection. Agriculture, 10(12), 610.
14- Aksoy, A., Demirezen, D., & Duman, F. (2005). Bioaccumulation, detection and analyses of heavy metal pollution in Sultan Marsh and its environment. Water, air, and soil pollution, 164, 241-255.
15- Bernardino, C. A., Mahler, C. F., Santelli, R. E., Freire, A. S., Braz, B. F., & Novo, L. A. (2019). Metal accumulation in roadside soils of Rio de Janeiro, Brazil: impact of traffic volume, road age, and urbanization level. Environmental monitoring and assessment, 191, 1-14.
16- Bi, X., Feng, X., Yang, Y., Li, X., Shin, G. P., Li, F., & Fu, Z. (2009). Allocation and source attribution of lead and cadmium in maize (Zea mays L.) impacted by smelting emissions. Environmental Pollution, 157(3), 834-839.
17- Botsou, F., Sungur, A., Kelepertzis, E., & Soylak, M. (2016). Insights into the chemical partitioning of trace metals in roadside and off-road agricultural soils along two major highways in Attica’s region, Greece. Ecotoxicology and Environmental Safety, 132, 101-110.
18- Debnath, B., Singh, W. S., & Manna, K. (2019). Sources and toxicological effects of lead on human health. Indian Journal of Medical Specialities, 10(2), 66-71.
19- Deng, J., & Wong, H. S. P. (2007). A compact SPICE model for carbon-nanotube field-effect transistors including nonidealities and its application—Part I: Model of the intrinsic channel region. IEEE Transactions on Electron Devices, 54(12), 3186-3194.
20- Gonzales, R.C. & Woods, R.E., 2002, Digital Image Processing, ‎ Pearson; 3rd edition (August 31, 2007), English, 976 pages.
21- Kakulu, S. E., & Jacob, J. O. (2006). Comparison of digestion methods for trace metal determination in moss samples. In Proceeding of the 1st National Conference of the Faculty of Science, University of Abuja (Vol. 77, p. 81).
22- Kumar, V., Sharma, A., Kaur, P., Sidhu, G. P. S., Bali, A. S., Bhardwaj, R., ... & Cerda, A. (2019). Pollution assessment of heavy metals in soils of India and ecological risk assessment: A state-of-the-art. Chemosphere, 216, 449-462.
23- Liao, B., Guo, Z., Probst, A., & Probst, J. L. (2005). Soil heavy metal contamination and acid deposition: experimental approach on two forest soils in Hunan, Southern China. Geoderma, 127(1-2), 91-103.
24- Liu, Y., Li, W., Wu, G., & Xu, X. (2011). Feasibility of estimating heavy metal contaminations in floodplain soils using laboratory-based hyperspectral data—A case study along Le’an River, China. Geo-spatial Information Science, 14(1), 10-16.
25- Ma, L. Q., Komar, K. M., Tu, C., Zhang, W., Cai, Y., & Kennelley, E. D. (2001). A fern that hyperaccumulates arsenic. Nature, 409(6820), 579-579.
26- Madejón, E., De Mora, A. P., Felipe, E., Burgos, P., & Cabrera, F. (2006). Soil amendments reduce trace element solubility in a contaminated soil and allow regrowth of natural vegetation. Environmental Pollution, 139(1), 40-52.
27- Mansour, R. S. (2014). The pollution of tree leaves with heavy metal in Syria. International Journal of ChemTech Research, 6(4), 2283-2290.
28- Merzlyak, M. N., Gitelson, A. A., Chivkunova, O. B., & Rakitin, V. Y. (1999). Non‐destructive optical detection of pigment changes during leaf senescence and fruit ripening. Physiologia plantarum, 106(1), 135-141.
29- Nadgórska–Socha, A., Kandziora-Ciupa, M., Trzęsicki, M., & Barczyk, G. (2017). Air pollution tolerance index and heavy metal bioaccumulation in selected plant species from urban biotopes. Chemosphere, 183, 471-482.
30- Nikolaevich, V. K. (2023). Central Russia heavy metal contamination model based on satellite imagery and machine learning. Компьютерная оптика, 47(1), 137-151.
31- Patel, K. S., Sharma, R., Dahariya, N. S., Yadav, A., Blazhev, B., Matini, L., & Hoinkis, J. (2015). Heavy metal contamination of tree leaves. American Journal of Analytical Chemistry, 6(08), 687.
32- Petronio, B. M., Pietrantonio, M., Pietroletti, M., & Cardellicchio, N. (2000). Environmental science and pollution research. In proceedings Seventh FECS Conference, Metal speciation and bio-availability in marine sediments of Nothern Adiatic sea (p. 320).
33- Scheuber, M., & Köhl, M. (2003). Assessment of non-wood-goods and services by cluster sampling. Advances in forest inventory for sustainable forest management and biodiversity monitoring, 157-171.
34- Sobura, S., Hejmanowska, B., Widłak, M., & Muszyńska, J. (2022). The Application of Remote Sensing Techniques and Spectral Analyzes to Assess the Content of Heavy Metals in Soil–A Case Study of Barania Góra Reserve, Poland. Geomatics and Environmental Engineering, 16(4), 187-213.
35- Tan, K., Wang, H., Chen, L., Du, Q., Du, P., & Pan, C. (2020). Estimation of the spatial distribution of heavy metal in agricultural soils using airborne hyperspectral imaging and random forest. Journal of hazardous materials, 382, 120987.
36- Wang, J., Hu, X., Shi, T., He, L., Hu, W., & Wu, G. (2022). Assessing toxic metal chromium in the soil in coal mining areas via proximal sensing: Prerequisites for land rehabilitation and sustainable development. Geoderma, 405, 115399.
37- Wang, X. S., & Qin, Y. (2007). Relationships between heavy metals and iron oxides, fulvic acids, particle size fractions in urban roadside soils. Environmental geology, 52, 63-69.
38- Wu, C., & Zhang, L. (2010). Heavy metal concentrations and their possible sources in paddy soils of a modern agricultural zone, southeastern China. Environmental Earth Sciences, 60, 45-56.
39- Wu, Y., Chen, J., Wu, X., Tian, Q., Ji, J., & Qin, Z. (2005). Possibilities of reflectance spectroscopy for the assessment of contaminant elements in suburban soils. Applied Geochemistry, 20(6), 1051-1059.
40- Xie, K. (1998). Determination of heavy metal contents in soil and plants around an urban environment and rural area [dissertation].
41- Zhang, Z., Liu, M., Liu, X., & Zhou, G. (2018). A new vegetation index based on multitemporal Sentinel-2 images for discriminating heavy metal stress levels in rice. Sensors, 18(7), 2172.
42- Zheng, G., Chen, J. M., Tian, Q. J., Ju, W. M., & Xia, X. Q. (2007). Combining remote sensing imagery and forest age inventory for biomass mapping. Journal of Environmental Management, 85(3), 616-623.