Abstract
This article contains the chemical and geographical data and figures for the chemical data in sediments of East Coast (Pattipulam to Dhevanampattinam) of Tamilnadu. The obtained data are related to the research article “Heavy Metal Assessment in Sediment Samples Collected From Pattipulam to Dhevanampattinam along the East Coast of Tamil Nadu Using EDXRF Technique” (Chandramohan et al., 2016) [1]. Chemical data are collected from Energy dispersive X-ray fluorescence spectrometer (EDXRF). Furthermore, the obtained chemical data describes it in more detail in the figures.
Keywords: Sediment, Heavy metals, EDXRF, Tamilnadu Coast
| Subject area | Physics, Chemistry, Geology |
| More specific subject area | Heavy metal contents in marine environment |
| Type of data | Table, Figures |
| How data was acquired | Energy Dispersive X-ray Fluorescence Spectrometer (EDXRF) |
| Data format | Raw |
| Experimental factors | The sediment samples were dried at 105 °C for 24 h, homogenized and sieved using a 63 μm in order to identify the geochemical concentrations. All powder samples were stored in desiccators until they were analyzed.One gram of the fine grinded sample and 0.5 g of boric acid (H3BO3) was mixed. The mixture was thoroughly grinded and pressed to a pellet of 25 mm diameter using a hydraulic press (20 tons) for EDXRF analysis. |
| Experimental features | Determination of concentration of Mg, Al, K, Ca, Ti, Fe, V, Cr, Mn, Co, Ni, Zn, As, Cd, Ba, La, Pb. |
| Data source location | Pattipulam to Devanampattinam, East Coast of Tamilnadu, India |
| Data accessibility | Data is with this article |
Value of the data
-
•
Data presented on the distribution, enrichment and sources of heavy metals in sediments can be useful to draw a base line data in marine environment.
-
•
Data shown here used as a tool for anthropogenic causes in heavy metal content and to identify common pollution sources.
-
•
Data shows that continuous monitoring and efforts of remediation might be required to improve the coastal environment near industrialized areas.
1. Data
The chemical data in sediments from Pattipulam to Devanampattinam along the East Coast of Tamilnadu is presented in Table 1. Table 2 gives the data on geographical information of the sampling points of the study area. Fig. 1 shows metals concentration levels in the sediment samples in polluted and unpolluted areas, and Fig. 2 shows the sampling points in the study area.
Table 1.
Heavy metal concentration (mg kg−1) in sediments from East coast of Tamilnadu, India.
| S. No | Location ID | Location | Mg | Al | K | Ca | Ti | Fe | V | Cr | Mn | Co | Ni | Zn | As | Cd | Ba | La | Pb |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| 1. | PPM | Pattipulam | 500 | 21,722 | 9200 | 8550 | 1043 | 5486 | 26.9 | 29.9 | 108.8 | 2.1 | 18.0 | 66.0 | 6.2 | 4.9 | 422.9 | 9.9 | 12.9 |
| 2. | DVN | Devaneri | 2600 | 27,900 | 8900 | 11,000 | 9889 | 21,836 | 162.2 | 61.9 | 386.9 | 7.1 | 20.3 | 58.7 | 7.0 | 3.2 | 362.8 | 123 | 14 |
| 3. | MAM | Mahabalipuram | 900 | 21,800 | 8300 | 9800 | 2122 | 9138 | 45.8 | 31.6 | 178.3 | 3.3 | 18.7 | 34.1 | 5.8 | 0 | 435.8 | 10.2 | 6.1 |
| 4. | KKM | Kokilamedu | 1500 | 24,000 | 9300 | 10,500 | 1911 | 7557 | 35.6 | 26.3 | 156.5 | 2.7 | 18.1 | 27.9 | 5.6 | 4.7 | 485.2 | 21.8 | 6.1 |
| 5. | KPM | Kalpakkam | 900 | 22,600 | 9300 | 9500 | 1352 | 6396 | 30.5 | 28.0 | 120.5 | 2.1 | 18.6 | 36.2 | 5.7 | 3.9 | 434.4 | 20.4 | 10 |
| 6. | VPC | Veppancheri | 2500 | 24,900 | 9000 | 9800 | 1614 | 7355 | 34.2 | 29.4 | 138.5 | 2.7 | 20.0 | 36.5 | 5.3 | 7.5 | 453.8 | 18.1 | 8.9 |
| 7. | TPM | Thenpattinam | 4200 | 23,700 | 8700 | 10,800 | 1543 | 7423 | 35.6 | 38.6 | 153.5 | 2.8 | 24.0 | 120.3 | 8.4 | 2.6 | 434.6 | 18.7 | 25.8 |
| 8. | MKM | Mudaliyarkuppam | 20 | 17,700 | 7200 | 7000 | 779 | 3945 | 23.8 | 21.7 | 88.9 | 1.4 | 19.7 | 50.1 | 5.5 | 0 | 302.9 | 7.5 | 7 |
| 9. | OKM | Odiyurkuppam | 200 | 18,300 | 8100 | 8100 | 661 | 4036 | 24.0 | 21.4 | 81.6 | 1.4 | 16.6 | 22.7 | 4.9 | 2.7 | 421.5 | 0 | 3.8 |
| 10. | APT | Alampara fort | 2400 | 23,200 | 8600 | 10,400 | 859 | 5513 | 28.0 | 23.6 | 113.2 | 2.1 | 20.6 | 44.2 | 5.5 | 4.6 | 436 | 2.4 | 7.3 |
| 11. | KPK | Kaipanikuppam | 600 | 17,800 | 7400 | 6400 | 614 | 3532 | 23.2 | 19.2 | 77.2 | 1.2 | 16.3 | 34.9 | 4.7 | 5.2 | 348.9 | 6 | 2.3 |
| 12. | FBH | French beach | 2600 | 20,200 | 7300 | 8500 | 1242 | 6283 | 29.5 | 27.8 | 136.5 | 2.3 | 19.3 | 34.9 | 4.7 | 7.1 | 335.4 | 4.8 | 4.5 |
| 13. | KMU | Koonimedu | 2500 | 21,800 | 7900 | 9400 | 1089 | 5694 | 28.2 | 32.3 | 123.9 | 2.1 | 21.8 | 121.9 | 8.3 | 0.2 | 337.1 | 1.1 | 24.7 |
| 14. | GCM | Ganapathichettikulam | 1600 | 19,900 | 7800 | 8100 | 845 | 4509 | 24.7 | 29.3 | 95.9 | 1.6 | 21.5 | 116.8 | 7.2 | 0 | 373.2 | 15.5 | 22.5 |
| 15. | ABH | Auroville beach | 1500 | 21,700 | 9100 | 10,400 | 1027 | 5431 | 26.1 | 26.7 | 109.2 | 2.0 | 18.3 | 44.2 | 5.6 | 4.8 | 426.8 | 12.7 | 7.5 |
| 16. | MPT | Muthiyalpet | 1600 | 21,500 | 8900 | 9300 | 942 | 4866 | 25.3 | 24.6 | 103.1 | 1.7 | 24.3 | 66.3 | 6.7 | 0 | 402.5 | 6.9 | 14 |
| 17. | PBH | Pondy beach | 1300 | 22,600 | 9300 | 9600 | 772 | 4649 | 24.9 | 25.9 | 95.1 | 1.8 | 25.8 | 83.8 | 6.7 | 2.5 | 442.4 | 10.8 | 18.6 |
| 18. | KEP | Keerapalayam | 1800 | 26,100 | 9500 | 12,500 | 753 | 5303 | 26.6 | 26.3 | 115.8 | 2.0 | 22.8 | 87.6 | 7 | 13.7 | 433.4 | 2.6 | 16.4 |
| 19. | PPT | Puthupettai | 1800 | 20,000 | 8000 | 8400 | 945 | 5433 | 27.3 | 30.7 | 102.0 | 2.1 | 19.1 | 65.9 | 6.3 | 0 | 450.4 | 13.2 | 14.2 |
| 20. | KIP | Kirumampakkam | 2500 | 23,100 | 7700 | 10,700 | 1632 | 8982 | 36.9 | 40.7 | 184.0 | 3.3 | 21.4 | 53.8 | 5.5 | 3.7 | 373.9 | 2.4 | 9.6 |
| 21. | TKA | Thazhankuda | 1900 | 15,800 | 7600 | 5800 | 376 | 3215 | 22.7 | 19.8 | 61.4 | 1.1 | 17.9 | 91.1 | 6.7 | 2.5 | 393.2 | 3 | 18.7 |
| 22. | DPM | Dhevanampattinam | 1200 | 21,500 | 7800 | 9700 | 1422 | 7604 | 35.0 | 45.6 | 138.3 | 2.9 | 22.1 | 70.3 | 6.3 | 1.5 | 401.6 | 20.2 | 11.7 |
| Average | 1665 | 21,719 | 8405 | 9284 | 1520 | 6554 | 35.3 | 30.1 | 130.4 | 2.4 | 20.2 | 62.2 | 6.2 | 3.4 | 404.9 | 15.1 | 12.1 | ||
| Minimum | 20 | 15,800 | 7200 | 5800 | 376 | 3215 | 22.7 | 19.2 | 61.4 | 1.1 | 16.3 | 22.7 | 4.7 | 0 | 302.9 | 0 | 2.3 | ||
| Maximum | 4220 | 27,900 | 9500 | 12,500 | 9889 | 21,836 | 162.2 | 61.9 | 386.9 | 7.1 | 25.8 | 121.9 | 8.4 | 13.7 | 485.2 | 123 | 25.8 | ||
| Crustal Average[3] | 15,000 | 80,000 | 26,600 | 22,100 | 4600 | 47,200 | 130 | 90 | 850 | 19 | 68 | 95 | 13 | 0.3 | 580 | 92 | 20 | ||
Table 2.
The Geographical latitude and longitude for the sampling locations of the study area.
| S. No | Location | Location ID | Latitude (N) | Longitude (E) |
|---|---|---|---|---|
| 1 | Pattipulam | PPM | 12°40׳51.27"N | 80°15׳19.35"E |
| 2 | Devaneri | DVN | 12°39׳19.32"N | 80°14׳49.68"E |
| 3 | Mahabalipuram | MAM | 12°37׳55.53"N | 80°14׳13.14"E |
| 4 | Kokilamedu | KKM | 12°34׳56.33"N | 80°13׳22.37"E |
| 5 | Kalpakkam | KPM | 12°30׳57.52"N | 80°11׳50.57"E |
| 6 | Veppancheri | VPC | 12°27׳58.97"N | 80°11׳16.29"E |
| 7 | Thenpattinam | TPM | 12°24׳42.28"N | 80° 9׳48.29"E |
| 8 | Mudaliyarkuppam | MKM | 12°21׳26.51"N | 80° 6׳52.67"E |
| 9 | Odiyurkuppam | OKM | 12°19׳35.89"N | 80° 5׳44.70"E |
| 10 | Alampara fort | APT | 12°16׳19.80"N | 80° 3׳16.00"E |
| 11 | Kaipanikuppam | KPK | 12°12׳42.65"N | 80° 1׳32.40"E |
| 12 | French beach | FBH | 12° 9׳2.75"N | 79°59׳11.44"E |
| 13 | Koonimedu | KMU | 12° 4׳59.37"N | 79°55׳53.55"E |
| 14 | Ganapathichettikulam | GCM | 12° 2׳45.84"N | 79°56׳46.86"E |
| 15 | Auroville beach | ABH | 11°59׳51.98"N | 79°55׳31.39"E |
| 16 | Muthiyalpet | MPT | 11°57׳43.22"N | 79°52׳42.65"E |
| 17 | Pondy beach | PBH | 11°56׳38.16"N | 79°52׳17.45"E |
| 18 | Keerapalayam | KEP | 11°54׳23.61"N | 79°51׳49.37"E |
| 19 | Puthupettai | PPT | 11°52׳45.44"N | 79°51׳19.75"E |
| 20 | Kirumampakkam | KIP | 11°50׳23.50"N | 79°51׳54.44"E |
| 21 | Thazhankuda | TKA | 11°46׳28.21"N | 79°49׳31.03"E |
| 22 | Dhevanampattinam | DPM | 11°44׳41.37"N | 79°49׳23.01"E |
Fig. 1.
Comparison of metals concentration levels in the sediment samples in polluted and unpolluted areas.
Fig. 2.
Location map.
2. Experimental design, materials and methods
2.1. Sample collections
Sediment samples were collected along the Bay of Bengal coastline, from Pattipulam to Devanampattinam coast during pre-monsoon condition. These samples were collected in pre-monsoon season, when sediment texture and ecological conditions can be clearly observed, when erosional activities are predominant, and sediments were not transported from the river and estuary towards the beach and marine. In order to ensure minimum disturbance of the upper layer, samples were collected by a Peterson grab sampler from 10 m water depths parallel to the shoreline. The grab sampler collects 10 cm thick bottom sediment layer from the seabed along the 22 stations.
Uniform quantity (about 2 kg) of sediment samples were collected from all the sampling stations. Sampling locations were selected to collect representative samples from all along the study area. Table 2 represents the geographical latitude and longitude for all the sampling locations of the study area. Care was taken to ensure that the collected sediments were not in contact with the metallic dredge of the sampler, and the top sediment layer was scooped with an acid washed plastic spatula. Sediment samples were stored in refrigerated at −4 °C until analysis [2]. Then pebbles, leaves and other foreign particles were removed.
2.2. EDXRF analysis
The samples were air dried at a temperature of 110 °C until constant weight, lightly ground in an agate mortar for homogenization and sieved to pass <63 µm (metals are most often associated with small grains) [3]. All powder samples were stored in desiccators until they were analyzed. One gram of the fine ground sample and 0.5 g of the boric acid (H3BO3) were mixed. The mixture was thoroughly ground and pressed to a pellet of 25 mm diameter using a hydraulic press (20 tons) for EDXRF analysis. Table 3 list the analysis of soil standard-2709a reference sample using EDXRF.
Table 3.
Results obtained from the analysis of soil standard-2709a reference sample using EDXRF (in mg kg−1).
| Element | Certified values | EDXRF values |
|---|---|---|
| Mg | 14,600.0 | 14,900.0 |
| Al | 72,100.0 | 68,400.0 |
| K | 20,500.0 | 19,100.0 |
| Ca | 19,100.0 | 16,500.0 |
| Ti | 3400.0 | 3100.0 |
| Fe | 33,600.0 | 33,900.0 |
| V | 110.0 | 98.8 |
| Cr | 130.0 | 112.1 |
| Mn | 529.0 | 568.2 |
| Co | 12.8 | 12.8 |
| Ni | 83.0 | 69.3 |
| Zn | 107.0 | 127.9 |
Conflict of interest
The authors declare no conflict of interest associated with this manuscript.
Acknowledgements
We are grateful to Dr. K. K. Satpathy, Head, Environment and Safety Division, HSEG, EIRSG, Indira Gandhi Centre for Atomic Research (IGCAR), Kalpakkam, Tamilnadu, India for EDXRF analysis at IGCAR and also our deep gratitude to Dr. M.V. R. Prasad, Head, EOHS, EnSD, HSEG, IGCAR, Kalpakkam for his keen interest, support and constant encouragement in EDXRF measurements.
Footnotes
Transparency data associated with this article can be found in the online version at doi:10.1016/j.dib.2016.09.047.
Transparency document. Supplementary material
Supplementary material
.
References
- 1.Chandramohan J., Chandrasekaran A., Senthilkumar G., Elango G., Ravisankar R. Heavy metal assessment in sediment samples collected from Pattipulam to Dhevanampattinam along the East Coast of Tamil Nadu Using EDXRF Technique. J. Heavy Metal. Toxic. Dis. 2016;1(2:8):1–5. [Google Scholar]
- 2.Ravisankar R., Sivakumar S., Chandrasekaran A., Kanagasabapathy K.V., Prasad M.V.R., Satapathy K.K. Statistical assessment of heavy metal pollution in sediments of east coast of Tamilnadu using Energy Dispersive X-ray Fluorescence Spectroscopy (EDXRF) Appl. Radiat. Isot. 2015;102:42–47. doi: 10.1016/j.apradiso.2015.03.018. [DOI] [PubMed] [Google Scholar]
- 3.Morillo J., Usero J., Gracia I. Heavy metal distribution in marine sediments from the southwest coast of Spain. Chemosphere. 2004;55(2004):431–442. doi: 10.1016/j.chemosphere.2003.10.047. [DOI] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Supplementary material


