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Open AccessOpen Access JUSTC Earth and Space Sciences 16 May 2022

Petroleum-contaminated soil extent recorded by δ15N and δ13C of plants and soils

  • 1.

    Key Laboratory of Subsurface Hydrology and Ecological Effect in Arid Region, Ministry of Education, School of Water and Environment, Chang’an University, Xi’an 710054, China

  • 2.

    School of Biological and Environmental Engineering, Xi’an University, Xi’an 710065, China

  • 3.

    Environmental Monitoring Station of Lanshan Branch, Rizhao Bureau of Ecology and Environment, Rizhao 276800, China

  • 4.

    Yunnan Key Laboratory of Earth System Science, Yunnan University, Kunming 650500, China

Cite this:
https://doi.org/10.52396/JUSTC-2021-0270
More Information
  • Author Bio:

    Zhoufeng Wang is a lecturer with Chang’an University. He received his Ph.D. degree from the Institute of Earth Environment, Chinese Academy of Sciences, in July 2008, and joined Chang’an University in the same year. His research interests focus on stable nitrogen isotope in the plant-soil system and the coupling mechanism of water, air, and heat transport in the critical zone

  • Corresponding author: E-mail: wangzf@chd.edu.cn
  • Received Date: 20 December 2021
  • Accepted Date: 18 April 2022
    • Available Online: 16 May 2022
    Abstract

  • Abstract

    Petroleum contamination in terrestrial environments caused by industrial activities is a significant problem that has received considerable attention. Carbon and nitrogen isotopic compositions (δ13C and δ15N) effectively describe the behavior of plants and soils under petroleum contamination stress. To better understand plant and soil responses to petroleum-contaminated soil, δ13C and δ15N values of the plants (Trifolium repens, Leguminosae with C3 photosynthesis pathway, and Agropyron cristatum with C4 photosynthesis pathway) and the soil samples under one-month exposure to different extents of petroleum contamination were measured. The results showed that petroleum contamination in the soil induced the soil δ15N values to increase and δ13C values to decrease; from 1.9‰ to 3.2‰ and from −23.6‰ to −26.8‰, respectively. However, the δ13C values of Agropyron cristatum decreased from −29.8‰ to −31.6‰, and the δ13C values of Trifolium repens remained relatively stable from −12.6‰ to −13.1‰, indicating that they have different coping strategies under petroleum-contaminated soil conditions. Moreover, the δ15N values of Trifolium repens decreased from 5.6‰ to 0.8‰ near the air δ15N values under petroleum-contaminated soil, which implies that their nitrogen fixation system works to reduce soil petroleum stress. The δ13C and δ15N values of Agropyron cristatum and Trifolium repens reflect changes in the metabolic system when they confront stressful environments. Therefore, stable isotopic compositions are useful proxies for monitoring petroleum-contaminated soil and evaluating the response of plants to petroleum contamination stress.

    Graphical abstract

    The δ13C and δ13N values of soil and plant changed with petroleum-contaminated soil concentration.

    Abstract

    Petroleum contamination in terrestrial environments caused by industrial activities is a significant problem that has received considerable attention. Carbon and nitrogen isotopic compositions (δ13C and δ15N) effectively describe the behavior of plants and soils under petroleum contamination stress. To better understand plant and soil responses to petroleum-contaminated soil, δ13C and δ15N values of the plants (Trifolium repens, Leguminosae with C3 photosynthesis pathway, and Agropyron cristatum with C4 photosynthesis pathway) and the soil samples under one-month exposure to different extents of petroleum contamination were measured. The results showed that petroleum contamination in the soil induced the soil δ15N values to increase and δ13C values to decrease; from 1.9‰ to 3.2‰ and from −23.6‰ to −26.8‰, respectively. However, the δ13C values of Agropyron cristatum decreased from −29.8‰ to −31.6‰, and the δ13C values of Trifolium repens remained relatively stable from −12.6‰ to −13.1‰, indicating that they have different coping strategies under petroleum-contaminated soil conditions. Moreover, the δ15N values of Trifolium repens decreased from 5.6‰ to 0.8‰ near the air δ15N values under petroleum-contaminated soil, which implies that their nitrogen fixation system works to reduce soil petroleum stress. The δ13C and δ15N values of Agropyron cristatum and Trifolium repens reflect changes in the metabolic system when they confront stressful environments. Therefore, stable isotopic compositions are useful proxies for monitoring petroleum-contaminated soil and evaluating the response of plants to petroleum contamination stress.

    • Public Summary

    • Petroleum-contaminated soil induced the soil δ15N values to increase and δ13C values to decrease.
    • The characteristics of plants influence plant δ13C and δ15N values under petroleum-contaminated soil.
    • The δ13C and δ15N values are useful proxies for monitoring petroleum-contaminated soil and evaluating the response of plants to the stress of petroleum contamination.

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    • References(70)
  • [1]
    Volkman J K, Revill A T. Oil pollution and microbial regulation. In: Environmental and Ecological Chemistry. Oxford, UK: EOLSS Publishers, 2002, 2: 1-9.
    [2]
    Thapa B, Kumar KC A, Ghimire A. A review on bioremediation of petroleum hydrocarbon contaminants in soil. Kathmandu University Journal of Science Engineering and Technology, 2012, 8 (1): 164–170. doi: 10.3126/kuset.v8i1.6056
    [3]
    Osuagwu A N, Okigbo A U, Ekpo I A, et al. Effect of crude oil pollution on growth parameters, chlorophyll content and bulbils yield in air potato (Dioscorea bulbifera L.). International Journal of Applied Science Technology, 2013, 3 (4): 37–42.
    [4]
    Hoang S A, Lamb D, Seshadri B, et al. Rhizoremediation as a green technology for the remediation of petroleum hydrocarbon-contaminated soils. Journal of Hazardous Materials, 2021, 401: 123282. doi: 10.1016/j.jhazmat.2020.123282
    [5]
    Ojimba T P. Determining the effects of crude oil pollution on crop production using stochastic translog production function in Rivers State, Nigeria. Journal of Development and Agricultural Economics, 2012, 4 (13): 346–360. doi: 10.5897/JDAE12.082
    [6]
    Obadimu C. Petroleum hydrocarbons contamination of surface water and groundwater in the Niger Delta Region of Nigeria. Journal of Environment Pollution and Human Health, 2018, 6 (2): 51–61. doi: 10.12691/jephh-6-2-2
    [7]
    Li T K, Liu Y, Lin S J, et al. Soil pollution management in China: A brief introduction. Sustainability, 2019, 11: 556. doi: 10.3390/su11030556
    [8]
    Hoang S A, Lamb D, Seshadri B, et al. Rhizoremediation as a green technology for the remediation of petroleum hydrocarbon-contaminated soils. Journal of Hazardous Materials, 2020, 401: 123282. doi: 10.1016/j.jhazmat.2020.123282
    [9]
    Techtmann S M, Zhuang M, Campo P, et al. Corexit 9500 enhances oil biodegradation and changes active bacterial community structure of oil-enriched microcosms. Applied & Environmental Microbiology, 2017, 83: e03462-16. doi: 10.1128/AEM.03462-16
    [10]
    Wang Y P, Liang J D, Wang J X, et al. Combining stable carbon isotope analysis and petroleum-fingerprinting to evaluate petroleum contamination in the Yanchang oilfield located on Loess Plateau in China. Environmental Science & Pollution Research, 2018, 25: 2830–2841. doi: 10.1007/s11356-017-0500-6
    [11]
    Varjani S J. Microbial degradation of petroleum hydrocarbons. Bioresource Technology, 2017, 223: 277–286. doi: 10.1016/j.biortech.2016.10.037
    [12]
    Ossai I C, Ahmed A, Hassan A, et al. Remediation of soil and water contaminated with petroleum hydrocarbon: A review. Environmental Technology & Innovation, 2020, 17: 100526. doi: 10.1016/j.eti.2019.100526
    [13]
    Khan S, Afzal M, Iqbal S, et al. Plant-bacteria partnerships for the remediation of hydrocarbon contaminated soils. Chemosphere, 2013, 90 (4): 1317–1332. doi: 10.1016/j.chemosphere.2012.09.045
    [14]
    Tran H T, Lin C, Bui X T, et al. Aerobic composting remediation of petroleum hydrocarbon-contaminated soil. Current and future perspectives. Science of The Total Environment, 2021, 753: 142250. doi: 10.1016/j.scitotenv.2020.142250
    [15]
    Gan S, Lau E V, Ng H K. Remediation of soils contaminated with polycyclic aromatic hydrocarbons (PAHs). Journal of Hazardous Materials, 2009, 172: 532–549. doi: 10.1016/j.jhazmat.2009.07.118
    [16]
    Ciric L, Philp J C, Whiteley A S. Hydrocarbon utilization within a diesel-degrading bacterial consortium. FEMS Microbiology Letters, 2010, 2: 116–122. doi: 10.1111/j.1574-6968.2009.01871.x
    [17]
    Lim M W, Lau E V, Poh P E. A comprehensive guide of remediation technologies for oil contaminated soil: Present works and future directions. Marine Pollution Bulletin, 2016, 109 (1): 14–45. doi: 10.1016/j.marpolbul.2016.04.023
    [18]
    Socolofsky S A, Gros J, North E, et al. The treatment of biodegradation in models of sub-surface oil spills: A review and sensitivity study. Marine Pollution Bulletin, 2019, 143: 204–219. doi: 10.1016/j.marpolbul.2019.04.018
    [19]
    Yang R Q, Liu G X, Chen T, et al. Characterization of the genome of a Nocardia strain isolated from soils in the Qinghai-Tibetan Plateau that specifically degrades crude oil and of this biodegradation. Genomics, 2019, 111 (3): 356–366. doi: 10.1016/j.ygeno.2018.02.010
    [20]
    Pereira E, Napp A P, Allebrandt S, et al. Biodegradation of aliphatic and polycyclic aromatic hydrocarbons in seawater by autochthonous microorganisms. International Biodeterioration & Biodegradation, 2019, 145: 104789. doi: 10.1016/j.ibiod.2019.104789
    [21]
    Técher D, Laval-Gilly P, Henry, et al. Contribution of Miscanthus x giganteus root exudates to the biostimulation of PAH degradation: An in vitro study. Science of the Total Environment, 2011, 409 (20): 4489–4495. doi: 10.1016/j.scitotenv.2011.06.049
    [22]
    Ghoreishi G, Alemzadeh A, Mojarrad M, et al. Bioremediation capability and characterization of bacteria isolated from petroleum contaminated soils in Iran. Sustainable Environment Research, 2017, 27 (4): 195–202. doi: 10.1016/j.serj.2017.05.002
    [23]
    Imron M F, Titah H S. Diesel biodegradation by microbial consortium of Vibrio alginolyticus and Acinetobacter lwoffii isolated from ship dismantling area in Tanjungjati coast, Madura, Indonesia. Iaetsd Journal for Advanced Research in Applied Sciences, 2018, 5 (1): 134–139.
    [24]
    Hasan H A, Abdullah S R, Kofli N T, et al. Interaction of environmental factors on simultaneous biosorption of lead and manganese ions by locally isolated Bacillus cereus. Journal of Industrial & Engineering Chemistry, 2016, 37: 295–305. doi: 10.1016/j.jiec.2016.03.038
    [25]
    Ebadi A, Khoshkholgh Sima N A, Olamaee M, et al. Effective bioremediation of a petroleum-polluted saline soil by a surfactant-producing Pseudomonas aeruginosa consortium. Journal of Advanced Research, 2017, 8: 627–633. doi: 10.1016/j.jare.2017.06.008
    [26]
    Vidonish J E, Zygourakis K, Masiello C A, et al. Thermal treatment of hydrocarbon-impacted soils: A review of technology innovation for sustainable remediation. Engineering, 2016, 2: 426–437. doi: 10.1016/J.ENG.2016.04.005
    [27]
    Jiang Y, Brassington K J, Prpich G, et al. Insights into the biodegradation of weathered hydrocarbons in contaminated soils by bioaugmentation and nutrient stimulation. Chemosphere, 2016, 161: 300–307. doi: 10.1016/j.chemosphere.2016.07.032
    [28]
    Xu X, Liu W, Tian S, et al. Petroleum hydrocarbon-degrading bacteria for the remediation of oil pollution under aerobic conditions: A perspective analysis. Frontiers in Microbiology, 2018, 9: 2885–2885. doi: 10.3389/fmicb.2018.02885
    [29]
    Imron M F, Kurniawan S B, Ismail N, et al. Future challenges in diesel biodegradation by bacteria isolates: A review. Journal of Cleaner Production, 2019, 248: 119716. doi: 10.1016/j.jclepro.2019.119716
    [30]
    Schmidt T C, Zwank L, Elsner M, et al. Compound-specific stable isotope analysis of organic contaminants in natural environments: A critical review of the state of the art, prospects, and future challenges. Analytical and Bioanalytical Chemistry, 2004, 378 (2): 283–300. doi: 10.1007/s00216-003-2350-y
    [31]
    Tian Z, Vila J, Yu M, et al. Tracing the biotransformation of polycyclic aromatic hydrocarbons in contaminated soil using stable isotope-assisted metabolomics. Environmental Science & Technology Letters, 2018, 5 (2): 103–109. doi: 10.1021/acs.estlett.7b00554
    [32]
    Druhan J L, Winnick M J, Thullner M. Stable isotope fractionation by transport and transformation. Reviews in Mineralogy and Geochemistry, 2019, 85: 239–264. doi: 10.2138/rmg.2019.85.8
    [33]
    Gray J R, Lacrampe-Couloume G, Gandhi D, et al. Carbon and hydrogen isotopic fractionation during biodegradation of methyl tert-butyl ether. Environmental Science & Technology, 2002, 36 (9): 1931–1938. doi: 10.1021/es011135n
    [34]
    Elsner M. Stable isotope fractionation to investigate natural transformation mechanisms of organic contaminants: Principles, prospects and limitations. Journal of Environmental Monitoring: JEM, 2010, 12 (11): 2005–2031. doi: 10.1039/c0em00277a
    [35]
    Gafni A, Rosenzweig R, Gelman F, et al. Anaerobic biodegradation of MTBE in a field site above the Israeli Coastal Aquifer: Evidence from δ13C compound-specific isotope analysis. Journal of Chemical Technology & Biotechnology, 2016, 91 (6): 1638–1645. doi: 10.1002/jctb.4914
    [36]
    Gao P, Li H B, Wilson C P, et al. Source identification of PAHs in soils based on stable carbon isotopic signatures. Critical Reviews in Environmental Science and Technology, 2018, 48: 923–948. doi: 10.1080/10643389.2018.1495983
    [37]
    Gafni A, Rosenzweig R, Gelman F, et al. Anaerobic biodegradation of MTBE in a field site above the Israeli Coastal Aquifer: Evidence from δ13C compound-specific isotope analysis. Journal of Chemical Technology & Biotechnology, 2016, 91: 1638–1645. doi: 10.1002/jctb.4914
    [38]
    Pi Y, Chen B, Bao M, et al. Microbial degradation of four dispersed crude oils by Rhodococcus sp. evaluated using carbon stable isotope analysis. Journal of Chemical Technology & Biotechnology, 2019, 94: 1800–1807. doi: 10.1002/jctb.5945
    [39]
    Huang C, Zeng Y, Luo X, et al. Tracing the sources and microbial degradation of PCBs in field sediments by a multiple-line-of-evidence approach including compound-specific stable isotope analysis. Water Research, 2020, 182: 115977. doi: 10.1016/j.watres.2020.115977
    [40]
    Hofstetter T B, Spain J C, Nishino S F, et al. Identifying competing aerobic nitrobenzene biodegradation pathways by compound-specific isotope analysis. Environmental Science & Technology, 2008, 42 (13): 4764–4770. doi: 10.1021/es8001053
    [41]
    Glaser B, Dreyer A, Bock M, et al. Source apportionment of organic pollutants of a highway-traffic-influenced urban area in Bayreuth (Germany) using biomarker and stable carbon isotope signatures. Environmental Science & Technology, 2005, 39 (11): 3911–3917. doi: 10.1021/es050002p
    [42]
    Chen Y X, Zhang X, Chang J, et al. Development of a novel method for enrichment of unsubstituted naphthalene and phenanthrene from crude oils to compound-specific stable isotope analysis. Analytical Methods, 2017, 9 (35): 5135–5139. doi: 10.1039/C7AY01257H
    [43]
    Qin G, Gong D, Fan M Y. Bioremediation of petroleum-contaminated soil by biostimulation amended with biochar. International Biodeterioration & Biodegradation, 2013, 85: 150–155. doi: 10.1016/j.ibiod.2013.07.004
    [44]
    Jiang X W, Wan L, Wang X S, et al. A multi-method study of regional groundwater circulation in the Ordos Plateau, NW China. Hydrogeology Journal, 2018, 26 (5): 1657–1668. doi: 10.1007/s10040-018-1731-4
    [45]
    Wang Z F, Gong C C, Bian Z H. The relationship between land use, land cover change, and the heat island effect in Xi’an city, China. Applied Ecology and Environmental Research, 2019, 17 (4): 7795–7806. doi: /10.15666/aeer/1704_77957806
    [46]
    Shen Y, Ji Y, Li C, et al. Effects of phytoremediation treatment on bacterial community structure and diversity in different petroleum-contaminated soils. International Journal of Environmental Research and Public Health, 2018, 15 (10): 2168. doi: 10.3390/ijerph15102168
    [47]
    Tsunekawa A, Liu G, Yamanaka N, et al. Restoration and Development of the Degraded Loess Plateau, China. Tokyo, Japan: Springer, 2014: 35–48.
    [48]
    Hu J, Liu W. An ion-exchange method for nitrogen isotope analysis of nitrate in soil. Soil Science Society of America Journal, 2014, 78 (3): 787–793. doi: 10.2136/sssaj2013.11.0478
    [49]
    Liu W G, Huang Y S, An Z S, et al. Summer monsoon intensity controls C4/C3 plant abundance during the last 35 ka in the Chinese Loess Plateau: Carbon isotope evidence from bulk organic matter and individual leaf waxes. Palaeogeography Palaeoclimatology Palaeoecology, 2005, 220: 243–254. doi: 10.1016/j.palaeo.2005.01.001
    [50]
    Liu W G, Feng X H, Ning Y F, et al. δ13C variation of C3 and C4 plants across an Asian monsoon rainfall gradient in arid northwestern China. Global Change Biology, 2005, 11 (7): 1094–1100. doi: 10.1111/j.1365-2486.2005.00969.x
    [51]
    O’Leary M H. Carbon isotopes in photosynthesis: Fractionation techniques may reveal new aspects of carbon dynamics in plants. Bioscience, 1988, 38 (5): 328–336. doi: 10.2307/1310735
    [52]
    Nel J A, Craine J M, Cramer M D. Correspondence between δ13C and δ15N in soils suggests coordinated fractionation processes for soil C and N. Plant and soil, 2018, 423 (1): 257–271. doi: 10.1007/s11104-017-3500-x
    [53]
    Liang Y T, Zhang X, Wang J, et al. Spatial variations of hydrocarbon contamination and soil properties in oil exploring fields across China. Journal of Hazardous Materials, 2012, 241: 371–378. doi: 10.1016/j.jhazmat.2012.09.055
    [54]
    Oyem I L R, Oyem I L. Effects of crude oil spillage on soil physico-chemical properties in Ugborodo Community. International Journal of Modern Engineering Research, 2013, 3 (6): 3336–3342.
    [55]
    Watson J S, Jones D M, Swannell R P J, et al. Formation of carboxylic acids during aerobic biodegradation of crude oil and evidence of microbial oxidation of hopanes. Organic Geochemistry, 2002, 33 (10): 1153–1169. doi: 10.1016/S0146-6380(02)00086-4
    [56]
    Twining C W, Taipale S J, Ruess L, et al. Stable isotopes of fatty acids: Current and future perspectives for advancing trophic ecology. Philosophical Transactions of the Royal Society B Biological Sciences, 2020, 375: 20190641. doi: 10.1098/rstb.2019.0641
    [57]
    Stahl W J. Use of 13C/12C analyses for the identification of the degradation of hydrocarbons by aerobic bacteria. Geochimica et Cosmochimica Acta, 1980, 44: 1903–1907. doi: 10.1016/0016-7037(80)90238-0
    [58]
    Zyakun A M, Brodskii E S, Baskunov B P, et al. Bioremediation of oil-polluted soils: Using the [13C/12C] ratio to characterize microbial products of oil hydrocarbon biodegradation. Applied Biochemistry and Microbiology, 2014, 50 (5): 483–491. doi: 10.1134/S0003683814040152
    [59]
    Bird M I, Pousai P. Variations of δ13C in the surface soil organic carbon pool. Global Biogeochemical Cycles, 1997, 11 (3): 313–322. doi: 10.1029/97GB01197
    [60]
    Deines P. The isotopic composition of reduced organic carbon. In: Handbook of Environmental Isotope Geochemistry: The Terrestrial Environment, A. Berlin: Elsevier, 1980: 329–406.
    [61]
    Robinson D, Handley L L, Scrimgeour C M, et al. Using stable isotope natural abundances (δ15N and δ13C) to integrate the stress responses of wild barley (Hordeum spontaneum C. Koch.) genotypes. Journal of Experimental Botany, 2000, 51 (342): 41–50. doi: 10.1093/jexbot/51.342.41
    [62]
    Pineda J E M, Twilley R R, Rivera-Monroy V H. Carbon (δ13C) and Nitrogen (δ15N) isotopic discrimination in mangroves in Florida Coastal Everglades as a function of environmental stress. Contributions in Marine Science, 2009, 38: 109–129.
    [63]
    Ihem E, Ahukemere C M, Ugochukwu N, et al. Differences in particle size distribution of soils of Northern Niger Delta of Nigeria as affected by crude oil pollution. International Journal of Research in Agriculture and Forestry, 2014, 1 (1): 16–20.
    [64]
    Angel R, Panhölzl C, Gabrel R, et al. Application of stable-isotope labelling techniques for the detection of active diazotrophs. Environmental Microbiology, 2018, 20 (1): 44–61. doi: 10.1111/1462-2920.13954
    [65]
    Sorkhoh N A, Ali N, Dashti N, et al. Soil bacteria with the combined potential for oil utilization, nitrogen fixation, and mercury resistance. International Biodeterioration & Biodegradation, 2010, 64 (3): 226–231. doi: 10.1016/j.ibiod.2009.10.011
    [66]
    John R C, Itah A Y, Essien J P, et al. Fate of nitrogen-fixing bacteria in crude oil contaminated wetland ultisol. Bulletin of Environmental Contamination and Toxicology, 2011, 87: 343. doi: 10.1007/s00128-011-0320-1
    [67]
    van Groenigen J, van Kessel C. Salinity-induced patterns of natural abundance carbon-13 and nitrogen-15 in plant and soil. Soil Science Society of America Journal, 2002, 66 (2): 489–498. doi: 10.2136/sssaj2002.4890
    [68]
    Roiloa S R, Antelo B, Retuerto R. Physiological integration modifies δ15N in the clonal plant Fragaria vesca, suggesting preferential transport of nitrogen to water-stressed offspring. Annals of Botany, 2014, 114 (2): 399–411. doi: 10.1093/aob/mcu064
    [69]
    Shan B Q, Zhang Y T, Cao Q L, et al. Growth responses of six leguminous plants adaptable in Northern Shaanxi to petroleum contaminated soil. Environmental Science, 2014, 35 (3): 1125–1130. doi: 10.13227/j.hjkx.2014.03.043
    [70]
    Polyak Y M, Bakina L G, Chugunova M V, et al. Effect of remediation strategies on biological activity of oil-contaminated soil: A field study. International Biodeterioration & Biodegradation, 2017, 126: 57–68. doi: 10.1016/j.ibiod.2017.10.004
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    Figure  1.  The Trifolium repens (a) and Agropyron cristatum (b) were collected from the experimental field after one month of growth. 0, 3000, 7000, and 10000 in the picture means the petroleum contamination concentration in the soil increased from 0, 3000, 7000 to 10000 mg/kg, respectively.

    Figure  2.  Soil δ13C variations under different petroleum pollution conditions with and without plants. Error bars indicate the standard deviation (n = 3). Different letters indicate significant differences among petroleum-contaminated soil concentrations ( p < 0.05).

    Figure  3.  Soil δ15N variations under different petroleum pollution conditions with and without plants. Error bars indicate the standard deviation (n = 3). Different letters indicate significant differences among petroleum-contaminated soil concentrations (p < 0.05).

    Figure  4.  δ13C changes of Agropyron cristatum and Trifolium repens under different soil petroleum pollution conditions. Error bars indicate the standard deviation (n = 3). Different letters indicate significant differences among petroleum-contaminated soil concentrations (p < 0.05).

    Figure  5.  δ15N changes of Agropyron cristatum and Trifolium repens under different soil petroleum pollution conditions. Error bars indicate the standard deviation (n = 3). Different letters indicate significant differences among petroleum-contaminated soil concentrations (p < 0.05).

    1S.  The δ15N values of the in-house standard. Five samples inserted one in-house standard to monitor the accuracy of the isotope-ratio mass spectrometer.

    [1]
    Volkman J K, Revill A T. Oil pollution and microbial regulation. In: Environmental and Ecological Chemistry. Oxford, UK: EOLSS Publishers, 2002, 2: 1-9.
    [2]
    Thapa B, Kumar KC A, Ghimire A. A review on bioremediation of petroleum hydrocarbon contaminants in soil. Kathmandu University Journal of Science Engineering and Technology, 2012, 8 (1): 164–170. doi: 10.3126/kuset.v8i1.6056
    [3]
    Osuagwu A N, Okigbo A U, Ekpo I A, et al. Effect of crude oil pollution on growth parameters, chlorophyll content and bulbils yield in air potato (Dioscorea bulbifera L.). International Journal of Applied Science Technology, 2013, 3 (4): 37–42.
    [4]
    Hoang S A, Lamb D, Seshadri B, et al. Rhizoremediation as a green technology for the remediation of petroleum hydrocarbon-contaminated soils. Journal of Hazardous Materials, 2021, 401: 123282. doi: 10.1016/j.jhazmat.2020.123282
    [5]
    Ojimba T P. Determining the effects of crude oil pollution on crop production using stochastic translog production function in Rivers State, Nigeria. Journal of Development and Agricultural Economics, 2012, 4 (13): 346–360. doi: 10.5897/JDAE12.082
    [6]
    Obadimu C. Petroleum hydrocarbons contamination of surface water and groundwater in the Niger Delta Region of Nigeria. Journal of Environment Pollution and Human Health, 2018, 6 (2): 51–61. doi: 10.12691/jephh-6-2-2
    [7]
    Li T K, Liu Y, Lin S J, et al. Soil pollution management in China: A brief introduction. Sustainability, 2019, 11: 556. doi: 10.3390/su11030556
    [8]
    Hoang S A, Lamb D, Seshadri B, et al. Rhizoremediation as a green technology for the remediation of petroleum hydrocarbon-contaminated soils. Journal of Hazardous Materials, 2020, 401: 123282. doi: 10.1016/j.jhazmat.2020.123282
    [9]
    Techtmann S M, Zhuang M, Campo P, et al. Corexit 9500 enhances oil biodegradation and changes active bacterial community structure of oil-enriched microcosms. Applied & Environmental Microbiology, 2017, 83: e03462-16. doi: 10.1128/AEM.03462-16
    [10]
    Wang Y P, Liang J D, Wang J X, et al. Combining stable carbon isotope analysis and petroleum-fingerprinting to evaluate petroleum contamination in the Yanchang oilfield located on Loess Plateau in China. Environmental Science & Pollution Research, 2018, 25: 2830–2841. doi: 10.1007/s11356-017-0500-6
    [11]
    Varjani S J. Microbial degradation of petroleum hydrocarbons. Bioresource Technology, 2017, 223: 277–286. doi: 10.1016/j.biortech.2016.10.037
    [12]
    Ossai I C, Ahmed A, Hassan A, et al. Remediation of soil and water contaminated with petroleum hydrocarbon: A review. Environmental Technology & Innovation, 2020, 17: 100526. doi: 10.1016/j.eti.2019.100526
    [13]
    Khan S, Afzal M, Iqbal S, et al. Plant-bacteria partnerships for the remediation of hydrocarbon contaminated soils. Chemosphere, 2013, 90 (4): 1317–1332. doi: 10.1016/j.chemosphere.2012.09.045
    [14]
    Tran H T, Lin C, Bui X T, et al. Aerobic composting remediation of petroleum hydrocarbon-contaminated soil. Current and future perspectives. Science of The Total Environment, 2021, 753: 142250. doi: 10.1016/j.scitotenv.2020.142250
    [15]
    Gan S, Lau E V, Ng H K. Remediation of soils contaminated with polycyclic aromatic hydrocarbons (PAHs). Journal of Hazardous Materials, 2009, 172: 532–549. doi: 10.1016/j.jhazmat.2009.07.118
    [16]
    Ciric L, Philp J C, Whiteley A S. Hydrocarbon utilization within a diesel-degrading bacterial consortium. FEMS Microbiology Letters, 2010, 2: 116–122. doi: 10.1111/j.1574-6968.2009.01871.x
    [17]
    Lim M W, Lau E V, Poh P E. A comprehensive guide of remediation technologies for oil contaminated soil: Present works and future directions. Marine Pollution Bulletin, 2016, 109 (1): 14–45. doi: 10.1016/j.marpolbul.2016.04.023
    [18]
    Socolofsky S A, Gros J, North E, et al. The treatment of biodegradation in models of sub-surface oil spills: A review and sensitivity study. Marine Pollution Bulletin, 2019, 143: 204–219. doi: 10.1016/j.marpolbul.2019.04.018
    [19]
    Yang R Q, Liu G X, Chen T, et al. Characterization of the genome of a Nocardia strain isolated from soils in the Qinghai-Tibetan Plateau that specifically degrades crude oil and of this biodegradation. Genomics, 2019, 111 (3): 356–366. doi: 10.1016/j.ygeno.2018.02.010
    [20]
    Pereira E, Napp A P, Allebrandt S, et al. Biodegradation of aliphatic and polycyclic aromatic hydrocarbons in seawater by autochthonous microorganisms. International Biodeterioration & Biodegradation, 2019, 145: 104789. doi: 10.1016/j.ibiod.2019.104789
    [21]
    Técher D, Laval-Gilly P, Henry, et al. Contribution of Miscanthus x giganteus root exudates to the biostimulation of PAH degradation: An in vitro study. Science of the Total Environment, 2011, 409 (20): 4489–4495. doi: 10.1016/j.scitotenv.2011.06.049
    [22]
    Ghoreishi G, Alemzadeh A, Mojarrad M, et al. Bioremediation capability and characterization of bacteria isolated from petroleum contaminated soils in Iran. Sustainable Environment Research, 2017, 27 (4): 195–202. doi: 10.1016/j.serj.2017.05.002
    [23]
    Imron M F, Titah H S. Diesel biodegradation by microbial consortium of Vibrio alginolyticus and Acinetobacter lwoffii isolated from ship dismantling area in Tanjungjati coast, Madura, Indonesia. Iaetsd Journal for Advanced Research in Applied Sciences, 2018, 5 (1): 134–139.
    [24]
    Hasan H A, Abdullah S R, Kofli N T, et al. Interaction of environmental factors on simultaneous biosorption of lead and manganese ions by locally isolated Bacillus cereus. Journal of Industrial & Engineering Chemistry, 2016, 37: 295–305. doi: 10.1016/j.jiec.2016.03.038
    [25]
    Ebadi A, Khoshkholgh Sima N A, Olamaee M, et al. Effective bioremediation of a petroleum-polluted saline soil by a surfactant-producing Pseudomonas aeruginosa consortium. Journal of Advanced Research, 2017, 8: 627–633. doi: 10.1016/j.jare.2017.06.008
    [26]
    Vidonish J E, Zygourakis K, Masiello C A, et al. Thermal treatment of hydrocarbon-impacted soils: A review of technology innovation for sustainable remediation. Engineering, 2016, 2: 426–437. doi: 10.1016/J.ENG.2016.04.005
    [27]
    Jiang Y, Brassington K J, Prpich G, et al. Insights into the biodegradation of weathered hydrocarbons in contaminated soils by bioaugmentation and nutrient stimulation. Chemosphere, 2016, 161: 300–307. doi: 10.1016/j.chemosphere.2016.07.032
    [28]
    Xu X, Liu W, Tian S, et al. Petroleum hydrocarbon-degrading bacteria for the remediation of oil pollution under aerobic conditions: A perspective analysis. Frontiers in Microbiology, 2018, 9: 2885–2885. doi: 10.3389/fmicb.2018.02885
    [29]
    Imron M F, Kurniawan S B, Ismail N, et al. Future challenges in diesel biodegradation by bacteria isolates: A review. Journal of Cleaner Production, 2019, 248: 119716. doi: 10.1016/j.jclepro.2019.119716
    [30]
    Schmidt T C, Zwank L, Elsner M, et al. Compound-specific stable isotope analysis of organic contaminants in natural environments: A critical review of the state of the art, prospects, and future challenges. Analytical and Bioanalytical Chemistry, 2004, 378 (2): 283–300. doi: 10.1007/s00216-003-2350-y
    [31]
    Tian Z, Vila J, Yu M, et al. Tracing the biotransformation of polycyclic aromatic hydrocarbons in contaminated soil using stable isotope-assisted metabolomics. Environmental Science & Technology Letters, 2018, 5 (2): 103–109. doi: 10.1021/acs.estlett.7b00554
    [32]
    Druhan J L, Winnick M J, Thullner M. Stable isotope fractionation by transport and transformation. Reviews in Mineralogy and Geochemistry, 2019, 85: 239–264. doi: 10.2138/rmg.2019.85.8
    [33]
    Gray J R, Lacrampe-Couloume G, Gandhi D, et al. Carbon and hydrogen isotopic fractionation during biodegradation of methyl tert-butyl ether. Environmental Science & Technology, 2002, 36 (9): 1931–1938. doi: 10.1021/es011135n
    [34]
    Elsner M. Stable isotope fractionation to investigate natural transformation mechanisms of organic contaminants: Principles, prospects and limitations. Journal of Environmental Monitoring: JEM, 2010, 12 (11): 2005–2031. doi: 10.1039/c0em00277a
    [35]
    Gafni A, Rosenzweig R, Gelman F, et al. Anaerobic biodegradation of MTBE in a field site above the Israeli Coastal Aquifer: Evidence from δ13C compound-specific isotope analysis. Journal of Chemical Technology & Biotechnology, 2016, 91 (6): 1638–1645. doi: 10.1002/jctb.4914
    [36]
    Gao P, Li H B, Wilson C P, et al. Source identification of PAHs in soils based on stable carbon isotopic signatures. Critical Reviews in Environmental Science and Technology, 2018, 48: 923–948. doi: 10.1080/10643389.2018.1495983
    [37]
    Gafni A, Rosenzweig R, Gelman F, et al. Anaerobic biodegradation of MTBE in a field site above the Israeli Coastal Aquifer: Evidence from δ13C compound-specific isotope analysis. Journal of Chemical Technology & Biotechnology, 2016, 91: 1638–1645. doi: 10.1002/jctb.4914
    [38]
    Pi Y, Chen B, Bao M, et al. Microbial degradation of four dispersed crude oils by Rhodococcus sp. evaluated using carbon stable isotope analysis. Journal of Chemical Technology & Biotechnology, 2019, 94: 1800–1807. doi: 10.1002/jctb.5945
    [39]
    Huang C, Zeng Y, Luo X, et al. Tracing the sources and microbial degradation of PCBs in field sediments by a multiple-line-of-evidence approach including compound-specific stable isotope analysis. Water Research, 2020, 182: 115977. doi: 10.1016/j.watres.2020.115977
    [40]
    Hofstetter T B, Spain J C, Nishino S F, et al. Identifying competing aerobic nitrobenzene biodegradation pathways by compound-specific isotope analysis. Environmental Science & Technology, 2008, 42 (13): 4764–4770. doi: 10.1021/es8001053
    [41]
    Glaser B, Dreyer A, Bock M, et al. Source apportionment of organic pollutants of a highway-traffic-influenced urban area in Bayreuth (Germany) using biomarker and stable carbon isotope signatures. Environmental Science & Technology, 2005, 39 (11): 3911–3917. doi: 10.1021/es050002p
    [42]
    Chen Y X, Zhang X, Chang J, et al. Development of a novel method for enrichment of unsubstituted naphthalene and phenanthrene from crude oils to compound-specific stable isotope analysis. Analytical Methods, 2017, 9 (35): 5135–5139. doi: 10.1039/C7AY01257H
    [43]
    Qin G, Gong D, Fan M Y. Bioremediation of petroleum-contaminated soil by biostimulation amended with biochar. International Biodeterioration & Biodegradation, 2013, 85: 150–155. doi: 10.1016/j.ibiod.2013.07.004
    [44]
    Jiang X W, Wan L, Wang X S, et al. A multi-method study of regional groundwater circulation in the Ordos Plateau, NW China. Hydrogeology Journal, 2018, 26 (5): 1657–1668. doi: 10.1007/s10040-018-1731-4
    [45]
    Wang Z F, Gong C C, Bian Z H. The relationship between land use, land cover change, and the heat island effect in Xi’an city, China. Applied Ecology and Environmental Research, 2019, 17 (4): 7795–7806. doi: /10.15666/aeer/1704_77957806
    [46]
    Shen Y, Ji Y, Li C, et al. Effects of phytoremediation treatment on bacterial community structure and diversity in different petroleum-contaminated soils. International Journal of Environmental Research and Public Health, 2018, 15 (10): 2168. doi: 10.3390/ijerph15102168
    [47]
    Tsunekawa A, Liu G, Yamanaka N, et al. Restoration and Development of the Degraded Loess Plateau, China. Tokyo, Japan: Springer, 2014: 35–48.
    [48]
    Hu J, Liu W. An ion-exchange method for nitrogen isotope analysis of nitrate in soil. Soil Science Society of America Journal, 2014, 78 (3): 787–793. doi: 10.2136/sssaj2013.11.0478
    [49]
    Liu W G, Huang Y S, An Z S, et al. Summer monsoon intensity controls C4/C3 plant abundance during the last 35 ka in the Chinese Loess Plateau: Carbon isotope evidence from bulk organic matter and individual leaf waxes. Palaeogeography Palaeoclimatology Palaeoecology, 2005, 220: 243–254. doi: 10.1016/j.palaeo.2005.01.001
    [50]
    Liu W G, Feng X H, Ning Y F, et al. δ13C variation of C3 and C4 plants across an Asian monsoon rainfall gradient in arid northwestern China. Global Change Biology, 2005, 11 (7): 1094–1100. doi: 10.1111/j.1365-2486.2005.00969.x
    [51]
    O’Leary M H. Carbon isotopes in photosynthesis: Fractionation techniques may reveal new aspects of carbon dynamics in plants. Bioscience, 1988, 38 (5): 328–336. doi: 10.2307/1310735
    [52]
    Nel J A, Craine J M, Cramer M D. Correspondence between δ13C and δ15N in soils suggests coordinated fractionation processes for soil C and N. Plant and soil, 2018, 423 (1): 257–271. doi: 10.1007/s11104-017-3500-x
    [53]
    Liang Y T, Zhang X, Wang J, et al. Spatial variations of hydrocarbon contamination and soil properties in oil exploring fields across China. Journal of Hazardous Materials, 2012, 241: 371–378. doi: 10.1016/j.jhazmat.2012.09.055
    [54]
    Oyem I L R, Oyem I L. Effects of crude oil spillage on soil physico-chemical properties in Ugborodo Community. International Journal of Modern Engineering Research, 2013, 3 (6): 3336–3342.
    [55]
    Watson J S, Jones D M, Swannell R P J, et al. Formation of carboxylic acids during aerobic biodegradation of crude oil and evidence of microbial oxidation of hopanes. Organic Geochemistry, 2002, 33 (10): 1153–1169. doi: 10.1016/S0146-6380(02)00086-4
    [56]
    Twining C W, Taipale S J, Ruess L, et al. Stable isotopes of fatty acids: Current and future perspectives for advancing trophic ecology. Philosophical Transactions of the Royal Society B Biological Sciences, 2020, 375: 20190641. doi: 10.1098/rstb.2019.0641
    [57]
    Stahl W J. Use of 13C/12C analyses for the identification of the degradation of hydrocarbons by aerobic bacteria. Geochimica et Cosmochimica Acta, 1980, 44: 1903–1907. doi: 10.1016/0016-7037(80)90238-0
    [58]
    Zyakun A M, Brodskii E S, Baskunov B P, et al. Bioremediation of oil-polluted soils: Using the [13C/12C] ratio to characterize microbial products of oil hydrocarbon biodegradation. Applied Biochemistry and Microbiology, 2014, 50 (5): 483–491. doi: 10.1134/S0003683814040152
    [59]
    Bird M I, Pousai P. Variations of δ13C in the surface soil organic carbon pool. Global Biogeochemical Cycles, 1997, 11 (3): 313–322. doi: 10.1029/97GB01197
    [60]
    Deines P. The isotopic composition of reduced organic carbon. In: Handbook of Environmental Isotope Geochemistry: The Terrestrial Environment, A. Berlin: Elsevier, 1980: 329–406.
    [61]
    Robinson D, Handley L L, Scrimgeour C M, et al. Using stable isotope natural abundances (δ15N and δ13C) to integrate the stress responses of wild barley (Hordeum spontaneum C. Koch.) genotypes. Journal of Experimental Botany, 2000, 51 (342): 41–50. doi: 10.1093/jexbot/51.342.41
    [62]
    Pineda J E M, Twilley R R, Rivera-Monroy V H. Carbon (δ13C) and Nitrogen (δ15N) isotopic discrimination in mangroves in Florida Coastal Everglades as a function of environmental stress. Contributions in Marine Science, 2009, 38: 109–129.
    [63]
    Ihem E, Ahukemere C M, Ugochukwu N, et al. Differences in particle size distribution of soils of Northern Niger Delta of Nigeria as affected by crude oil pollution. International Journal of Research in Agriculture and Forestry, 2014, 1 (1): 16–20.
    [64]
    Angel R, Panhölzl C, Gabrel R, et al. Application of stable-isotope labelling techniques for the detection of active diazotrophs. Environmental Microbiology, 2018, 20 (1): 44–61. doi: 10.1111/1462-2920.13954
    [65]
    Sorkhoh N A, Ali N, Dashti N, et al. Soil bacteria with the combined potential for oil utilization, nitrogen fixation, and mercury resistance. International Biodeterioration & Biodegradation, 2010, 64 (3): 226–231. doi: 10.1016/j.ibiod.2009.10.011
    [66]
    John R C, Itah A Y, Essien J P, et al. Fate of nitrogen-fixing bacteria in crude oil contaminated wetland ultisol. Bulletin of Environmental Contamination and Toxicology, 2011, 87: 343. doi: 10.1007/s00128-011-0320-1
    [67]
    van Groenigen J, van Kessel C. Salinity-induced patterns of natural abundance carbon-13 and nitrogen-15 in plant and soil. Soil Science Society of America Journal, 2002, 66 (2): 489–498. doi: 10.2136/sssaj2002.4890
    [68]
    Roiloa S R, Antelo B, Retuerto R. Physiological integration modifies δ15N in the clonal plant Fragaria vesca, suggesting preferential transport of nitrogen to water-stressed offspring. Annals of Botany, 2014, 114 (2): 399–411. doi: 10.1093/aob/mcu064
    [69]
    Shan B Q, Zhang Y T, Cao Q L, et al. Growth responses of six leguminous plants adaptable in Northern Shaanxi to petroleum contaminated soil. Environmental Science, 2014, 35 (3): 1125–1130. doi: 10.13227/j.hjkx.2014.03.043
    [70]
    Polyak Y M, Bakina L G, Chugunova M V, et al. Effect of remediation strategies on biological activity of oil-contaminated soil: A field study. International Biodeterioration & Biodegradation, 2017, 126: 57–68. doi: 10.1016/j.ibiod.2017.10.004
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