Phytoremediation: Water Treatment Using Plants

Conducting phytoremediation procedures is important to recover potable water from water supplies that can be tapped within the Navajo Nation’s borders. At present, a significant portion of the already limited water within Navajo Nation’s borders is non potable due to pollution, especially heavy metal pollution from mines and industrial processes [1]. However, many of the Diné people have no other choice but to use this polluted water in their everyday lives due to lack of viable alternatives. Additionally, heavy metals are problematic as aquatic pollutants due to their ability to persist in the environment for generations and high potential to accumulate and reach toxic concentrations across the food chain [2]. As a result, crops and livestock grown with contaminated water ultimately will pass on concentrated toxins to the people that consume them. The primary heavy metals found in Navajo Nation include uranium and arsenic, according to EPA tests of unregulated wells [3]. Uranium is associated with kidney damage as a result of acute exposure and increased cancer risk due to radioactive decay [4]. Arsenic has been linked to a wide range of symptoms for both chronic and acute exposure [5]. Chronic exposure to arsenic has been known to cause hyperpigmentation, developmental effects, diabetes, pulmonary disease, and cardiovascular disease [5]. Acute arsenic exposure has been linked to vomiting, abdominal pain, diarrhea, numbness in the limbs, and death [5]. Continuous exposure to such toxic heavy metals has already had significant health impacts on the Diné people. Normally, the Diné have rates of cancer incidence lower than the average American. However, they are far more likely to pass away from certain types of cancers than a non-Hispanic white person living in the same state (7.2 times for gallbladder cancer, 4.4 times for stomach cancer, 2.1 times for kidney cancer, and 1.8 times for liver cancer), likely due to chronic exposure to heavy metals [1].

 

Figure 1: Distribution of wells, abandoned uranium mines, and major cities in the Navajo Nation.

 

Phytoremediation can help solve heavy metal contamination of the Diné water supply by making use of plants with the ability to absorb heavy metals from soil and water. First, the plants to be used must be selected based on the extent and type of pollution [6]. For example, surface level contamination can be treated with shallow-rooted plants, and subsurface and/or groundwater contamination would be best handled by deep-rooted plants [6]. The plants must also be able to effectively uptake the contaminant in question and grow to maturity despite the presence of toxins [6]. Additionally, the plants should be fast-growing to maximize plant turnover, especially considering that multiple rounds of phytoremediation (at least one per growing season) are usually needed over the span of 2-5 years [6][7].

Figure 2: A general overview of how phytoremediation works [7]

 

Once selected, these plants can be grown directly on the site of contamination (e.g. abandoned mines, contaminated wells) or grown in artificial environments with exposure to heavy metals [7]. They will uptake the heavy metal ions into their structures, removing the contaminants from the local environment [8]. Once the plants have fully matured, they are harvested and incinerated to prevent re-release of heavy metals into the environment [7][8]. Plants native to the area, such as prickly pear cactus, sunflowers, tobacco, and tumbleweed, can be used to prevent the risk of invasive species endangering ecosystems and ensure ecological compatibility during the growing season of the accumulator plants. [8][11][12][13][14][15].

 

For a classroom or project-based setting, students can learn how to select and grow different phytoremediation candidates. The plants can be grown in a variety of settings to show the concept of phytoremediation while tailoring to the school’s resources and the age of the students. The most advanced level would be allowing high school and college students to directly plant on sites with actual contaminated water and soil, and using water and soil quality tests to measure the changes in contamination levels over time. Conversely, for elementary school students, the concept can be simulated with colored water and potted plants, so the students can watch the changes in color as the “contaminant” is absorbed. Students can make use of trial and error to find the optimal plants and growing conditions that maximize removal of contaminants, enabling them to gain new skills in acquiring clean water for their own farms and families in the future.

 

Comparison of actual phytoremediation candidates already in Navajo Nation: [16][17][18][19][20][21][22][23][24][25][26][27][28]

Name: Depth of Remediation Compatible heavy metals Potential Effectiveness Other considerations
Opuntia phaeacantha

Navajo Name:

Common Name: Prickly Pear Cactus

Very shallow, has shallow root system to soak up any runoff before it dries Lead

Copper

Manganese

Cadmium

Zinc

Nickel Copper  Chromium

Moderate as a plant, has more explored potential when harvested May be sharp, hazard for children

Excellent for dry climates

Helianthus sp.

Navajo Name: Hoshniteelí

Common Name: Sunflower

Deep, taproot reaches 4 feet Radioactive Uranium

Arsenic

Lead

Mercury

Cadmium

Low to high, variable with soil conditions (ideally moist and well-drained with pH 6) Will need more water to germinate but otherwise drought-hardy
Rumex crispus

Navajo Name: Dziłnát’oh

Common Name: Navajo Tobacco

Shallow depths due to shallow root system with mostly lateral spread Arsenic

Uranium

Cadmium

Lead

Zinc

Copper

Iron

Manganese Magnesium

High Considered a weed

Toxic to animals

Not suitable for small children

Salsola tragus

Navajo Name: Ch’ildeeníní

Common Name: Tumbleweed

Very deep, with main taproot reaching 6 feet Arsenic

Uranium

Chromium

Copper

Nickel

Zinc

High Considered a weed

May be sharp, hazard for small children

 

Phytoremediation shows promise as a method to acquire clean water that can be taught to and used by the future generation of the Diné people, helping promote greater water stability and agricultural productivity for future generations.

 

Works Cited:

[1] Ingram, J. C., Jones, L., Credo, J., & Rock, T. (2020, May). Uranium and arsenic unregulated water issues on Navajo Lands. Journal of vacuum science & technology. Retrieved November 30, 2022, from https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7083651/

[2] Lenntech. (2020). Heavy Metals. Lenntech Water treatment & purification. Retrieved November 30, 2022, from https://www.lenntech.com/processes/heavy/heavy-metals/heavy-metals.htm

[3] Environmental Protection Agency. (2022). Water sources table with MCLS. Navajo Nation Contaminated Unregulated Water Sources. Retrieved November 30, 2022, from https://www.epa.gov/sites/default/files/2016-06/documents/watersourcestable-with-mcls.pdf

[4] Depleted UF6 Management Program. (2022). Uranium Health Effects. Uranium health effects. Retrieved November 30, 2022, from https://web.evs.anl.gov/uranium/guide/ucompound/health/index.cfm

[5] World Health Organization. (2018, February 15). Arsenic. World Health Organization. Retrieved November 30, 2022, from https://www.who.int/news-room/fact-sheets/detail/arsenic

[6] Chirakkara, R. A., & Reddy, K. R. (2015). Plant Species Identification for Phytoremediation of Mixed Contaminated Soils. University of Illinois Chicago . Retrieved November 30, 2022, from https://cemmlab.webhost.uic.edu/2153-5515-0000282.pdf

[7] Environmental Protection Agency. (2012, September). A Citizen's Guide to Phytoremediation. United States Environmental Protection Agency . Retrieved November 30, 2022, from https://www.epa.gov/sites/default/files/2015-04/documents/a_citizens_guide_to_phytoremediation.pdf

[8] Yan, A., Wang, Y., Tan, S. N., Yusof, M. L. M., Ghosh, S., & Chen, Z. (2020, April 30). Phytoremediation: A Promising Approach for Revegetation of Heavy Metal-Polluted Land. Frontiers Journal. Retrieved November 30, 2022, from https://www.frontiersin.org/articles/10.3389/fpls.2020.00359/full

[9] Hunce, S. Y., Clemente, R., & Bernal, M. P. (2019, April 30). Energy Production Potential of Phytoremediation Plant Biomass: Helianthus annuus and Silybum marianum. Science Direct. Retrieved November 30, 2022, from https://www.sciencedirect.com/science/article/abs/pii/S0926669019302808

[10] Naval Research Laboratory. (2022). Technology for Innovative Entrepreneurs & Businesses. TechLink. Retrieved November 30, 2022, from https://techlinkcenter.org/technologies/zero-waste-method-for-recovering-heavy-metals-and-rare-earth-elements-from-ash/e81412b8-2791-4c8b-a2a0-a496d479f733

[11] New Mexico State University. (2018). Selected plants of navajo rangelands. NMSU. Retrieved November 30, 2022, from https://navajorange.nmsu.edu/perform_search.php?name=&genus=&species=&plantType=0&growingSeason=0&flowerColor=0

[12] The University of Georgia, National Park Service, Invasive Plant Atlas of New England, Invasive Plant Control Inc., USDA Forest Service, USDA NRCS PLANTS Database, Lady Bird Johnson Wildflower Center, National Association of Exotic Pest Plant Councils, Plant Conservation Alliance, & Biota of North America Program. (2018, October). The Common Sunflower. Invasive Plant Atlas. Retrieved November 30, 2022, from https://www.invasiveplantatlas.org/subject.html?sub=5688

[13] Derbe, T. (2017). Cactus Potential in Heavy Metal (Cb and Cd) Removal In Water Sample Collected From Rural Area Around Adigrat Town. Semantic Scholar. Retrieved November 30, 2022, from https://www.semanticscholar.org/paper/Cactus-Potential-in-Heavy-Metal-(Pb-and-Cd)-Removal-Derbe/e3353e1c65dc70b4b072c10d47cd3f762f7c0ca1

[14] Alaboudi, K. A., Ahmed, B., &; Brodie, G. (2018, June 19). Phytoremediation of Pb and Cd contaminated soils by using sunflower (helianthus annuus) plant. Science Direct. Retrieved November 30, 2022, from https://www.sciencedirect.com/science/article/pii/S0570178318300174

[15] Gardea-Torresdey, J. L., De la Rosa, G., Peralta-Videa, J. R., Montes, M., Cruz-Jimenez, G., & Cano-Aguilera, I. (2005, January 4). Differential uptake and transport of trivalent and hexavalent chromium by Tumbleweed (Salsola Kali). Archives of environmental contamination and toxicology. Retrieved November 30, 2022, from https://pubmed.ncbi.nlm.nih.gov/15696348/

[16] United States Department of Agriculture. (2018, April 11). Plant Guide. USDA Natural Resources . Retrieved November 30, 2022, from https://plants.sc.egov.usda.gov/home/plantProfile?symbol=SATR12

[17] De la Rosa, G., Parsons, J. G., Martinez-Martinez, A., Peralta-Videa, J. R., & Gardea-Torresdey, J. L. (2006, March 15). Spectroscopic study of the impact of arsenic speciation on arsenic/phosphorus uptake and plant growth in tumbleweed (Salsola Kali). Environmental science & technology. Retrieved November 30, 2022, from https://www.ncbi.nlm.nih.gov/pmc/articles/PMC2535608/

[18] De la Rosa, G., Peralta-Videa, J. R., Cruz-Jimenez, G., Cano-Aguilera, I., Gardea-Torresdey, J. L., & Parsons, J. G. (2006). CHARACTERIZATION OF CU, NI AND ZN UPTAKE IN TUMBLEWEED (S. kali) FOR PHYTOREMEDIATION PURPOSES. Revista Mexicana de Ingeniería Química. Retrieved November 30, 2022, from http://rmiq.org/ojs311/index.php/rmiq/article/view/2041

[19] Chang, P., Kim, K.-W., Yoshida, S., & Kim, S.-Y. (2005, September). Uranium Accumulation of Crop Plants Enhanced by Citric Acid. Research Gate. Retrieved November 30, 2022, from https://www.researchgate.net/publication/7528111_Uranium_Accumulation_of_Crop_Plants_Enhanced_by_Citric_Acid

[20] Yang, Y., Ge, Y., Zeng, H., Zhou, X., Peng, L., & Zeng, Q. (2017, August 3). Phytoextraction of cadmium-contaminated soil and potential of regenerated tobacco biomass for recovery of cadmium. PubMed Central. Retrieved November 30, 2022, from https://www.ncbi.nlm.nih.gov/pmc/articles/PMC5543114/

[21] Nahar, N., Rahman, A., Nawani, N., Ghosh, S., & Mandal, A. (2017, November). Phytoremediation of arsenic from the contaminated soil using transgenic tobacco plants expressing ACR2 gene of Arabidopsis thaliana. Journal of plant physiology. Retrieved November 30, 2022, from https://pubmed.ncbi.nlm.nih.gov/28818758/

[22] Stojanovic, M. D., Mihajlovic, M. L., Milojkovic, J. V., Lopcic, Z. R., Adamovic, M., & Stankovic, S. (2012, March 21). Efficient phytoremediation of uranium mine tailings by tobacco. SpringerLink. Retrieved November 30, 2022, from https://link.springer.com/article/10.1007/s10311-012-0362-6

[23] Gier, L. J. (1940, November). Root systems of bright belt tobacco - JSTOR. JSTOR. Retrieved November 30, 2022, from https://www.jstor.org/stable/2436905

[24] Marathe, S. (2019, December 2). Potential of sunflower to extract heavy metals from leachate. International Journal of Geosciences. Retrieved November 30, 2022, from https://www.scirp.org/journal/paperinformation.aspx?paperid=97130

[25] Chen, L., Yang, J.-yan, & Wang, D. (2020, April 7). Phytoremediation of uranium and cadmium contaminated soils by Sunflower (helianthus annuus L.) enhanced with biodegradable chelating agents. ScienceDirect. Retrieved November 30, 2022, from https://www.sciencedirect.com/science/article/abs/pii/S0959652620315389

[26] Mohler, C. L. (2022, September 21). Sunflower, common. SARE. Retrieved November 30, 2022, from https://www.sare.org/publications/manage-weeds-on-your-farm/common-sunflower/#sunflower-identification

[27] Amari, A., Alalwan, B., Eldirderi, M. M., Mnif, W., & Rebah, F. B. (2019, December 23). Cactus material-based adsorbents for the removal of heavy metals and ... IOP Science. Retrieved November 30, 2022, from https://iopscience.iop.org/article/10.1088/2053-1591/ab5f32

[28] Nisa, A. U. (2017, February 14). Biosorption of heavy metals from sewage effluent using prickly pear cactus. Zenodo. Retrieved November 30, 2022, from https://zenodo.org/record/2760660