Within the scope of rehabilitation of mined-out sites and possible occurrence of phytomining in the Philippines, this study examined the natural vegetation of the mined-out sites of Adnama Mining Resources Incorporated in Urbiztondo, Claver, Surigao del Norte for potential nickel (Ni) hyperaccumulator species. Both the soil and vegetation (leaf samples) were evaluated by assaying the heavy metal Ni. This work revealed that Ni concentrations of the soils in the mined-out sites studied were comparable among each other having no or little distinctiveness. Also, it emphasized a large variation in Ni concentration in the plant samples collected depending on the plant species and the sites.
Results show that native plant species Sowa-sowa (Unidentified), Magotambis (Syzygium longiflorum), and Artocarpus sp. have the potential being hyperaccumulators of Ni with concentrations 218 μg g-1, 142 μg g-1, and 123 μg g-1 respectively. No plant species sampled satisfied the requirement of Ni hyperaccumulation which is 1000 μg g-1.
Table of Contents
Rationale
Objectives
Methods
Findings
Implications
LITERATURE CITED
Appendix
Rationale
Plants as a tool for environmental remediation is a basic idea which is practiced in old times and cannot anymore be traced to any particular source (Raskin et al., 1997). Some plants can tremendously accumulate high levels of certain metal ions (Cullaj et al., 2004). The ability of these plants to accumulate very high concentrations of metals from soils provides the basis for remediation of the contaminated sites where toxic metals are removed from contaminated areas thru extraction. The traditional approach of remediating a polluted and contaminated site is extremely expensive and can range from $600,000 to $3,000,000 depending on the extent of pollution, whereas Phytoremediation costs 20 times less expensive (Paz-Alberto & Sigua, 2013). Plant species are considered hyperaccumulators if it accumulates more than 1000 mg/kg (dry weight) or 100-fold greater than in those common nonaccumulator plants (Shaw, 1989; Baker, 1995; Salt et al., 1995; Lasat, 2002)
Claver, Surigao del Norte in the Caraga Region is one of the places to have the biggest iron mineral deposit throughout Asia and has attracted many mining companies. It has at least three (3) mining companies of which Nickel is one of the main heavy metals being mined-out. Adnama Mining Resources Incorporated (AMRI) is one of the companies established in the area which is engaged in Nickel mining.
There were several heavy metals hyperaccumulator plant species already identified (Fernando et al., 2014) and reported worldwide by scientists in several countries. The application of this remediation strategy (using these identified plant species) however, is limited by the climactic and geological conditions of the site to be remediated such as the temperature, soil type, and altitude; it is further limited by the availability of the metals in the soil for uptake (Schmoger et al., 2000). Hence, this study has been conducted to provide insight for the rehabilitation of the mined-out areas of AMRI.
Objectives
The primary objective of the study was to identify potential nickel hyperaccumulator native plant species that can be used as a tool for soil remediation in mined-out areas of Adnama Mining Resources Incorporated (AMRI) located at Brgy. Urbiztondo, Claver, Surigao del Norte, Philippines. Specifically it aimed to (1) assess the biophysical characteristics of the mined-out areas of AMRI with special reference on Nickel, (2) evaluate the nickel content of tissue samples of selected native plant species as potential Ni hyperaccumulator and (3) recommend native plant species suitable for restoration of mined-out areas operated by AMRI.
Methods
Samples of soil and plant species were collected from the mined-out areas of AMRI at Brgy. Urbiztondo, Claver, Surigao del Norte, Philippines. After field surveys and visual observations, four (4) sampling sites were identified. Three of these sampling sites were in the mined out areas still having natural vegetation while one sampling site was in the area that was not yet mined during the conduct of the study which served as a reference.
The sampling sites were established in the mined-out areas where natural vegetation is still present. Sampling area was divided into four sampling stations each with 10 x 10 meters. Topographical locations of the established sampling sites are modeled in Figure 1a and Figure 1b. First sampling site was established at the summit of the mined-out area, second was established at the backslope, and the third was established at the footslope. The fourth sampling site was established at backslope in an area which was not mined-out a few kilometers from the three (3) sampling sites. Established sampling sites 1, 2, and 3 are located at Block 2 Mined-out Area of AMRI while sampling site 4 was established at Block 3 of AMRI.
Four composite soil samples in four different strata (0-20, 20-40, 40-60, 60-100 cm depth) at each established site were collected and placed separately in properly labeled plastic bags. Soil samples were subjected to standard methods and procedures of soil sample preparation of the AMRI Assay Laboratory.
After the preparation of the collected soil samples, it was then subjected to XRF method of analysis for total Ni analysis. Standard methods and procedures of the AMRI Assay Laboratory were followed for total nickel analysis.
Healthy mature leaves of indigenous plants that were covered by the 10x10m established sampling site at each site were randomly collected. Leaf samples were taken from 5 different plants of the same species per sampling point to make a composite sample. In cases where the population of one species of plant was less than 5 in the sampling site, a composite sample was collected from the maximum number of plants present. Leaf samples were washed with distilled water in the field, air dried, kept inside labeled paper bags and was transported to the Department of Agronomy and Soil Science, Visayas State University. Samples were oven-dried at 70°C for at least 2 days before grounded and placed in labeled small paper bags.
Grounded leaf samples were screened (semi-quantitative test) for nickel accumulation. A 0.5 g of each grounded plant sample was wet digested with 6 M hydrochloric acid overnight. The digest were diluted to 100mL volume solution. Aliquots were taken and added with 1mL of 1% dimethylglyoxime dissolved in 95% ethanol. Formation of pink or magenta color indicated exceptionally high (above 1,000 μg g-1) concentration of Ni in the dry plant matter (Fernando et al., 2014).
Standard nickel previously added with 1 % dimethylglyoxime, dissolved in 95% ethanol was set-up for UV-Vis analysis. The wavelength of this sample served as the basis in qualitatively determining the plant samples for possible nickel hyperaccumulation.
Top ten (10) samples were considered from the 81 plant samples that had undergone semi-quantitative screening for nickel accumulation. These top ten (10) samples were then identified through the detailed photographs sent and examined by the AMRI’s Rainforestation Officer, Mr. Cyril Reginald Canonoy. Other plant species which were difficult to identify were identified in the family level by Forester Hernando L. Mondal of the College of Forestry and Environmental Sciences in Visayas State University
The top ten (10) samples were then analyzed quantitatively for total nickel concentration using the UV-Vis Absorption Spectroscopy. Kept, grounded samples of these top ten were ashed at 600°C for 2 hours followed by the addition of 1mL concentrated hydrochloric acid. The digests were diluted and aliquots were taken then 1mL of 1% of the nickel-specific colorimetric reagent, dimethylglyoxime, dissolved in 95% ethanol was added. After which, samples were taken for nickel analysis through UV-Vis Absorption Spectroscopy. Standard methods and procedures were adapted from Salas et al., (1998).
Levels of μg g-1 of Ni in leaf samples were compared to the criteria for classifying metal hyperaccumulator plant species. To be considered hyperaccumulating, the plants must have accumulated 1000 mg/kg or 1000 μg g-1 (dry weight) or 100-fold greater than in those common nonaccumulator plants of Ni (Shaw, 1989; Baker, 1995; Salt et al., 1995; Lasat, 2002; Baker and Brooks, 1989).
Frequently asked questions
What is the rationale behind the study?
The study explores the use of plants for environmental remediation, a practice rooted in ancient times. Some plants have the remarkable ability to accumulate high levels of metal ions, offering a cost-effective alternative to traditional remediation methods. Traditional methods can cost between $600,000 to $3,000,000, while phytoremediation can cost 20 times less. Plants accumulating more than 1000 mg/kg (dry weight) are classified as hyperaccumulators.
What is the study about?
The study focuses on identifying native plant species in the mined-out areas of Adnama Mining Resources Incorporated (AMRI) in Claver, Surigao del Norte, Philippines, that can hyperaccumulate nickel. This region is known for its significant iron mineral deposits and nickel mining operations.
What are the main objectives of this research?
The study aims to: 1) Assess the biophysical characteristics, especially nickel content, of mined-out areas in AMRI. 2) Evaluate the nickel content in tissue samples of selected native plant species to determine their potential as nickel hyperaccumulators. 3) Recommend suitable native plant species for the restoration of mined-out areas operated by AMRI.
How was the study conducted?
Soil and plant samples were collected from mined-out areas of AMRI. Four sampling sites were identified, including three in mined-out areas with natural vegetation and one reference site in an unmined area. Soil samples were analyzed using the XRF method for total nickel content. Plant samples were screened for nickel accumulation through semi-quantitative tests, followed by quantitative analysis using UV-Vis Absorption Spectroscopy.
What are the key methods used in the analysis?
The methods include: Field surveys and visual observations to identify sampling sites; Collection of composite soil samples at different depths; XRF analysis for total nickel in soil; Collection of mature leaf samples from indigenous plants; Semi-quantitative screening of leaf samples for nickel; Identification of plant species; Quantitative analysis of selected samples using UV-Vis Absorption Spectroscopy; and Statistical analysis (ANOVA) using STATISTICA software.
What criteria are used to classify hyperaccumulator plants?
Plants are considered hyperaccumulators if they accumulate more than 1000 mg/kg (dry weight) of a particular metal, or 100-fold greater than levels found in common non-accumulator plants. In this context, the focus is on nickel accumulation.
- Citation du texte
- Joshua Reambonanza (Auteur), Dr. Felix M. Salas (Auteur), 2015, Vegetation Assessment of AMRI Mined-out Sites for Potential Nickel Hyperaccumulator Species, Munich, GRIN Verlag, https://www.grin.com/document/302739
