Heavy Metal (Pb, Cd, Zn, Cu, Cr, Fe and Mn) Content in Textile Sludge in Gazipur, Bangladesh
S.A.M. Waliul Hoque
M. Saiful Islam
The present research was carried out with eight specimens
of sludge from Apex Weaving and Finishing Mills Ltd. Gazipur, Bangladesh,
to determine the concentration of heavy metals (Pb, Cd, Zn, Cu, Cr, Fe
and Mn) in the sludge samples and an assessment was made with the heavy
metal content in agricultural soil. Atomic Absorption Spectrometry (AAS)
method was employed for the analysis of Pb, Cd, Cr, Zn, Cu and UV-Spectrophotometric
method was used for Fe and Mn, respectively. The mean concentration of
lead (Pb), cadmium (Cd), chromium (Cr) was 79.13, 6.27, 4.35 mg kg-1
and for zinc (Zn), copper (Cu), iron (Fe) and manganese (Mn) it was 7.90,
1.34, 195.2 and 3.97 g kg-1, respectively. All the heavy metal
concentrations except chromium in the sludge samples were higher than
that of in agricultural soil. In addition, the study concluded that pre-treatment
process for reducing the amount of heavy metal is mandatory before the
sludge can be used as a soil conditioner or fertilizer in the agricultural
to cite this article:
M.M. Islam, M.A. Halim, S. Safiullah, S.A.M. Waliul Hoque and M. Saiful Islam, 2009. Heavy Metal (Pb, Cd, Zn, Cu, Cr, Fe and Mn) Content in Textile Sludge in Gazipur, Bangladesh. Research Journal of Environmental Sciences, 3: 311-315.
The textile industry, the flagship of Bangladesh-now earns more than 70% of
the country`s total export income. A recent report also revealed that Bangladesh`s
RMG (Ready Made Garments) exports to the world markets reached an all time high
value of over USD 9.35 billion in the end of 2007 (BGMEA,
2008). This textile and dyeing industries now viewed as a major environmental
threat in the industrial area of Bangladesh and they contribute huge amounts
of sludge in wastewater treatment processes (Karim et
al., 2006). Although characteristics of sludge depend on the wastewater
treatment process and sludge stabilization methods, it contains substantial
amounts of toxic heavy metals (Chen et al., 2005;
Singh et al., 2004). Another recent investigation
reported that elevated levels of heavy metals in vegetables are found from the
areas having long term uses of treated or untreated wastewater (Sharma
et al., 2006, 2007).
Heavy metals are very harmful because of their non-biodegradable nature, long
biological half-lives and their potential to accumulate in different body parts
(Manaham, 2005; Wilson and Pyatt, 2007).
Excessive accumulation of heavy metals in agricultural soils through wastewater
irrigation, may not only result in soil contamination, but also affect food
quality and safety (Muchuweti et al., 2006). Some
research also confirmed that heavy metals such as Cd, Pb, Cu, Zn and Ni have
carcinogenic or toxic effects on human beings and environment (Trichopoulos,
2001; Turkdogan et al., 2002; Kocasoy
and Sahin, 2007).
The management of sludge is becoming increasingly difficult due to the presence
of heavy metals (Zorpas et al., 2008). It is now
established that application of sludge into land can increase soil water-holding
capacity, decrease soil bulk density, increase soil aeration and root penetrability
and stimulate soil microorganism activity (Kvarnstrom et
al., 2000). In addition, land utilization of sludge could represent
a step forward to more sustainable farming practices and municipal waste management.
Achieving this purpose it is pivotal to know the heavy metal content in textile
sludge as without investigating toxic substances it is not feasible to use sludge
as a soil conditioner or fertilizer in agricultural land.
MATERIALS AND METHODS
Sludge Sample Collection
The sludge samples were collected from Apex Weaving and Finishing
Mills Ltd. Gazipur, Bangladesh in mid-January, 2004. The collected samples
were stored into separate plastic container and stored at ambient temperature
prior to treatment. The sludge samples were homogenized by manual mixing,
air-dried for 24 h, disaggregated using a pestle and mortar made by porcelain
to pass through a 2 mm mesh sieve.
Digestion of Sample with Aqua-Regia
An aliquot of 0.200 g of powdered sludge of each sample was taken
in a silica crucible (150 cm3). Then 1M concentrated hydrochloric
acid (9 cm3) was added followed by 1 M concentrated nitric
acid (3 cm3). The content of the crucible was carefully heated
in sandbath nearly to dryness in fumehood. After cooling the crucible
at room temperature, deionized water was added to the sample and was filtered
through a filter paper (Whatman No. 42). The filtrate was collected in
a measuring flask and was preserved for the determination of Pb, Cd, Zn,
Cu, Cr, Fe and Mn. All regents used were Merck, Analytical Grade (AR)
including standard stock solutions of known concentrations of different
Heavy Metal Analysis
Heavy metals analysis were carried out using AAS (Perkin Elmer AAnalyst
400). The AAS was calibrated for all the metals by running different concentrations
of standard solutions. Average values of three replicates were taken for each
determination. The detection limits for Pb, Cd, Zn, Cu and Cr were 3.0, 1.60,
1.60, 3.0 and 3.0 mg L-1, respectively. Iron determination was carried
out by hydroxylamine and with 1, 10 phenanthroline at pH 3.2-3.3. At pH between
2.9 and 3.5, rapid color was formed in the presence of an excess phenanthroline
and the reddish-orange iron (II) complex absorbs at 515 nm (Greenberg
et al., 1998). A quantitative estimation of Mn in the digested samples
was carried out using a UV Spectrophotometer (Sequoia-Tuner, Model-390) following
permanganate oxidation method at 522 nm. Because of its distinctive color and
stability, permanganate ion is preferably used as the determination form for
RESULTS AND DISCUSSION
The present study found that the average concentration of lead in the sludge
samples was 79.13 mg kg-1 although the content of lead in the eight
sludge samples ranged from 73.61-86.02 mg kg-1 in Table
1. This result revealed that examined sludge samples contained relatively
higher amount of Pb than that of agricultural soil. Threshold natural background
of Pb in agricultural soil in China is ≤35 mg kg-1 (Wong
et al., 2002). Kabata-Pendias and Pendias (2000)
reported that the maximum content of Pb was 50 mg kg-1 in light soils
used for cultivation.
Usually, sludge contains high concentration of cadmium, because wastewater
discharged from mill contains cadmium from dyes. The average concentration of
cadmium of the sludge samples was 6.27 mg kg-1 in Table
1. The permissible level of Cd in agricultural soils set by Dutch authorities
is 1 to 5 mg kg-1 (Chen et al., 1997).
Natural background level of Cd in agricultural soil in China is ≤0.20 mg
kg-1 (Wong et al., 2002). The values
of Cd found in the present investigation were higher than those of above critical
value set by other researchers. In addition, some cadmium compounds are able
to leach through soils to ground water. When cadmium compounds bind the sediments
of rivers, they can be more easily bioaccumulated or re-dissolved when sediments
are disturbed, such as during flooding. Therefore, the use of sludge as a soil
conditioner or fertilizer in arable soils can cause severe pollution with Cd
and the production of crops and vegetables may be at a risk.
|| The concentrations of heavy metals in all sludge samples
The maximum Zn value in light soil used in cultivation in India given by Kabata-Pendias
and Pendias (2000) was 100 mg kg-1. The threshold natural background
value of Zn in crop soils and paddy soils in China is ≤100 mg kg-1.
In Table 2, the concentration of Zn was found 7906.5 mg kg-1
in the sludge samples, which was higher than those of permissible levels given
by different nations. Similarly, the Cu content in the sludge samples was 1347.7
mg kg-1 which was also extremely higher than that of in China (≤35
mg kg-1) and India (20-30 mg kg-1). Some well documented
studies disclosed that heavy metals such as zinc (Zn) and copper (Cu) are the
principal elements restricting the use of sludge for agricultural purposes (Su
and Wong, 2003; Udom et al., 2004; Dai
et al., 2007).
The average concentration of chromium (Cr) in these samples was 4.35 mg kg-1.
The maximum content of Cr reported by Kabata-Pendias and Pendias
(2000) in soil used in cultivation was 100 mg kg-1. Natural background
of Cr in agricultural soils in China is ≤ 90 mg kg-1. The Cr content
in soils obtained from the present study was lower than the permissible levels
recommended by the above sources.
Long term exposure of iron from the sludge into soils may contaminate it and
change the soil structure and thus make it harmful for cultivation. Kisku
et al. (2000) found the concentrations of Fe in agricultural soils
in India varying from 289.3-338.5 mg kg-1 dry weight. Samantaray
et al. (2001) reported that the Fe content ranged from 1422.5-1593.0
mg kg-1 in agricultural soils near a metalliferous chromite mine
spoil in India. The Fe contents found in the sludge samples were higher than
that of the study by above two researchers. However, the safe limit for iron
is not available in Indian and Chinese standard. The average amount of manganese
(Mn) in the sludge samples was 3974.1 mg kg-1 which was very higher
than the range of uncontaminated soil in India (Table 2).
The concentrations of Cd, Zn, Cu and Mn in the sludge samples were exceed
the safe limit set by India and China whereas Pb and Cr found within the
safe limit (Table 2). The present study failed to compare
the results with Bangladesh standard as the Department of Environment;
Government of Bangladesh has not yet established any standard for heavy
metal content in agricultural soil. Therefore, it is very necessary to
establish a safe or standard limit for the concentration of heavy metal
in sludge that can be used as a fertilizer as well as soil conditioner.
Awashthi, S.K., 2000. Prevention of Food Adulteration Act no 37 of 1954. Central and State Rules as Amended for 1999. 3rd Edn., Ashoka Law House, New Delhi.
BGMEA, 2008. Bangladesh Garments Manufactures and Exporters Association Statistical Report, 2(2) April, 2008. http://www.just-style.com/factsheet.aspx?id=276.
Bowen, H.J.M., 1966. Trace Elements in Biochemistry. 1st Edn., Academic Press, New York, ISBN-13: 9780003686463.
Chen T.B., J.W.C. Wong, H.Y. Zhou and M.H. Wong, 1997. Assessment of trace metal distribution and contamination in surface soils of Hong Kong. Environ. Pollut., 96: 61-68.
Chen, Y., C. Wang and Z. Wang, 2005. Residues and source identification of persistent organic pollutants in farmland soils irrigated by effluents from biological treatment plants. Environ. Int., 31: 778-783.
Dai, J.Y., M.Q. Xu, J.P. Chen, X.P. Yang and Z.S. Ke, 2007. PCDD/F, PAH and heavy metals in the sewage sludge from six wastewater treatment plants in Beijing. China Chemosphere, 66: 353-361.
Greenberg, A.E., L.S. Clesceri, R.R. Trussell and M.A. Franson, 1998. Standard Methods for the Examination of Water and Wastewater. 20th Edn., American Public Health Association, Washington, DC., ISBN: 0875531318.
Kabata-Pendias, A. and H. Pendias, 2000. Trace Elements in Soils and Plants. 3rd Edn., CRC Press Inc., Boca Raton, FL., USA., ISBN-13: 9780849315756, Pages: 431.
Karim, M.M., A.K. Das and S.H. Lee, 2006. Treatment of colored effluent of the textile industry in Bangladesh using zinc chloride treated indigenous activated carbons. Anal. Chimica. Acta., 576: 37-42.
Kisku, G.C., S.C. Barman and S.K. Bhargava, 2000. Contamination of soil and plants with potentially toxic effluents irrigated with mixed industrial effluent and its impact on the environment. Water Air Soil Pollut., 120: 121-137.
CrossRef | Direct Link |
Kocasoy, G. and V. Sahin, 2007. Heavy metal removal from industrial wastewater by clinoptilolite. J. Environ. Sci. Health Part A, 42: 2139-2146.
Kvarnstrom, E., C Morel, J. Fardeau and J. Morel, 2000. Changes in the phosphorus availability of a chemically precipitated urban sewage sludge as a result of different dewatering processes. Waste Manage. Res., 18: 249-258.
Manaham, S.E., 2005. Environmental Chemistry. 8th Edn., Lewis Publisher, Boca Raton, Florida, ISBN 1566706335.
Muchuweti, M., J.W. Birkett, E. Chinyanga, R. Zvauya, M.D. Scrimshaw and J.N. Lester, 2006. Heavy metal content of vegetables irrigated with mixtures of wastewater and sewage sludge in Zimbabwe: Implications for human health. Agric. Ecosyst. Environ., 112: 41-48.
CrossRef | Direct Link |
SEPA, 1995. Environmental quality standard for soils. State Environmental Protection Administration, China. GB15618-1995.
Samantaray, S., G.R. Rout and P. Das, 2001. Heavy metal and nutrient concentration in soil and plants growing on a metalliferous chromite minespoil. Environ. Technol., 22: 1147-1154.
Direct Link |
Sharma, R.K., M. Agrawal and F. Marshall, 2007. Heavy metal contamination of soil and vegetables in suburban areas of Varansi, India. Ecotoxicol. Environ. Safety, 66: 258-266.
Sharma, R.K., M. Agrawal and F.M. Marshall, 2006. Heavy metal contamination in vegetables grown in wastewater irrigated areas of varanasi, India. Bull. Environ. Contaminat. Toxicol., 77: 312-318.
CrossRef | Direct Link |
Singh, K.P., D. Mohan, S. Sinha and R. Dalwani, 2004. Impact assessment of treated/untreated wastewater toxicants discharged by sewage treatment plants on health, agricultural and environmental quality in the wastewater disposal area. Chemosphere, 55: 227-255.
CrossRef | PubMed | Direct Link |
Singh, R.K. and M. Agrawal, 2005. Atmospheric depositions around a heavily industrialized area in a seasonally dry tropical environment of India. Environ. Pollut., 138: 142-152.
Su, D.C. and J.W.C. Wong, 2003. Chemical speciation and phytoavailability of Zn, Cu, Ni and Cd in soil amended with fly ash-stabilized sewage sludge. Environ. Int., 29: 895-900.
Trichopoulos, D., 2001. Epidemiology of Cancer. In: Cancer: Principles and Practice of Oncology, DeVita, V.T. (Ed.). Lippincott Company, Philadelphia, ISBN: 0-781-72229-2, pp: 231-258.
Turkdogan, M.K., F. Kilicel, K. Kara, I. Tuncer and I. Uygan, 2002. Heavy metals in soil, vegetables and fruits in the endemic upper gastrointestinal cancer region of Turkey. Environ. Toxicol. Pharmacol., 13: 175-179.
Udom, B.E., J.S.C. Mbagwu, J.K. Adesodun and N.N. Agbim, 2004. Distributions of zinc, copper, cadmium and lead in a tropical ultisol after long-term disposal of sewage sludge. Environ. Int., 30: 467-470.
CrossRef | Direct Link |
Wilson, B. and F.B. Pyatt, 2007. Heavy metal dispersion, persistence, and bioaccumulation around an ancient copper mine situated in Anglesey. UK. Ecotoxicol. Environ. Safety, 66: 224-231.
Wong, S.C., X.D. Li, G. Zhang, S.H. Qi and Y.S. Min, 2002. Heavy metals in agricultural soils of the pearl river delta, South China. Environ. Pollut., 119: 33-44.
Zorpas, A.A., V.J. Inglezakis and M. Loizidou, 2008. Heavy metals fractionation before, during and after composting of sewage sludge with natural zeolite. Waste Manage., 28: 2054-2060.