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Soil Enzyme Responses and Crop Productivity Indices Assessment in Agricultural Soil Impacted with Heavy Metals

Received: 29 March 2024     Accepted: 20 May 2024     Published: 29 September 2024
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Abstract

The present study assessed the productivity of cultivated garden vegetable among other ecological assessments in soil samples impacted with heavy metals. Assay of soil enzyme responses showed the activity of: catalase, peroxidase, lipase and ureasewith corresponding OD reading of 0.750, 2.05, 0.22 and 1.704 respectively. There were noticeable increases in the activity of ureaseandperoxidasewhilecatalaseandlipaseactivitywererelativelylowinthesampledsoil. Out of the 321g of the vegetable seedstested for viability, 45% representing 144.45g was used for the planting and further experiment. After three days of cultivation, germination process was recorded faster in the T. oleifera potted ridge while Amaranthus and Solanum sp seed took 3-4 day for break full dormancy. Determination of total chlorophyll a and b in the selected vegetables showed a correlative increase in chlorophyll a and b in soils contaminated with Zn, Cu and Fe in all the cultivated vegetables: T. oleifera, Amaranthus and Solanum sp, respectively. There are significant increase in total cholorphyl a (0.9mg/g) and b (0.8mg/g) contents from the results when compared with the control experiment as other soil contaminated with heavy metals such as: Pb, and As repressed the selected vegetables cultivated in the soil samples. However total chlorophyll a was seems lightly higher than cholophyl b in all the selected vegetable cultivated in soil. Analysis on the impact of heavy metals on the shootlength of the cultivated vegetables analysed for thirty-one days showed regressive increase in the shootlength of the cultivated vegetables as the period of harvest increases from 0-31 when compared with the control experiment. However Cd and As had the most estimated impact on the vegetables in all the cultivated soils and its impact progresses as the period of harvest increases. Dry matter weight contents of the cultivated vegetables cultivated in the polluted soils were analysed; also the same index was assessed in the vegetables from the unpolluted soils. There was a significant increase in the dry matter contents of the cultivated vegetables in soil polluted with Cu, Fe and Zn respectively. However, dry matter contents were seen progressively low in vegetables cultivated in soils polluted with Cd, As and Pb. When compared with the control experiment. The results from the present study have shown the vulnerability of agricultural soil and cultivated vegetables to effluent from industrial bias sources used for irrigation and its impact on agricultural productivity.

Published in American Journal of Chemical and Biochemical Engineering (Volume 8, Issue 2)
DOI 10.11648/j.ajcbe.20240802.11
Page(s) 34-44
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2024. Published by Science Publishing Group

Keywords

Heavy Metals, Vegetable, Enzymes, Pollution

1. Introduction
Enormous quantities of noxious pollutants have been released into surrounding over the last few decades. Among these pollutants, heavy metals (HMs), polycyclic aromatic hydrocarbons (PAHs) and total petroleum hydrocarbons (TPH) represent the major pollutants of terrestrial environment . The threat of pollutants not only from natural sources such as seeps but also from anthropogenic activities such as spillages from effluent treatment plants and other emissions, endangers the terrestrial biodiversity . Soil and its inhabitant organisms tend to accumulate different dietary and waterborne contaminants including heavy metals, polycyclic aromatic hydrocarbon and other organic compound such as Anthracene etc from the environment which they live in .
Heavy metals otherwise known as the trace metals due to their relativity in abundance and bioavaiability are metals with relatively high atomic mass and thus which reflect in their atomic weights examples includes Arsenic, beryllium, cadmium, chromium, lead, manganese, mercury, nickel, and selenium . They take part in bio-geochemical reactions and are transported between compartments by natural processes, the rate of which are at times greatly altered by human activities . They persist in nature and can cause damage or death in animals, humans, and plants even at very low concentrations (1 or 2 micrograms in some cases. The metals cannot be metabolized by natural means. Chemical industries are key source of heavy metals (Osuji and Onajeke, 2004). The peculiar ability of heavy metals is to accumulate without being noticed to levels of toxicity . Heavy metals are connected with severe health abnormalities such as nephrotoxicity, neurotoxicity and malignancies of various types (Goyer, 1996). Lead (Pb) interferes with haem biosynthesis 68. It inhibits the activity of 2-amino laevulinic acid dehydratase which leads to accumulation of protoporphyrin in the red blood cell . Cadmium can expediently substitute zinc in several enzymes consequently changing their configuration and inhibiting catalytic function .
With the increasing human population and change in the feeding culture of people, there has been increased need for food supply. This with the need for quality food vitamin has increased the demand for vegetable foods e.g green spinaches and its products . The global consumption of vegetable and derived vegetable products for example has generally increased during recent decades . The cage herbarium sector has grown very rapidly during the past 20 years and is presently undergoing rapid changes in response to pressures from globalization and growing demand for vegetable products in both developing and developed countries .
It has been predicted that vegetable consumption in developing countries will increase by 57 percent, from 62.7 million metric tons in 1997 to 98.6 million in 2020 .
Vegetables enjoy a good reputation as a nutritious and healthy food. The consumption of vegetables is recommended because it is a good source of antioxidants among other beneficial phytochemical components which has been associated with health benefits due to its cardio-protective effects . Vegetables also contain vitamins, mineral and other trace beneficial elements which play essential role in human health . However, the levels of contaminants in vegetables and its poor management are of particular interest because of the potential risk to humans who consume them. High level of heavy metals bioaccumulation in vegetables to such a degree that it becomes toxic to human when ingested. In Nigeria, data on heavy metals and other potential hazardous compounds in both aquaculture area and open cultured are lacking . The safety and health state of the vegetables consumed are not aware of. Estimation of heavy metals in the environment is important because of the clinical significant of these recalcitrant in foods especially when they passed on to human being through the consumption of vegetables and vegetable products . Agricultural practices and its bountifulness can only improve when the integrity of the surrounding soil is not compromised. The present study provides information on the impact of trace metals on the growth and productivity of vegetables sampled from three farms in Enugu metropolis.
2. Materials and Methods
2.1. Materials
All the chemicals, reagents and equipments used in the present study were of analytical grade and products of designated companies of BDh, Sigma, May and Baker; the equipments are properly calibrated at each use and stored at regulated condition.
2.2. Soil Sample Collection
Soil sample were collected around three different parts within Enugu metropolis (Long.140N, SE 4) as described by Ezenwelu et al. and as contained in ATSDR ; the samples were pooled together in a clean container whereas debris were selected off initially. There taken to the laboratory for further analysis.
2.3. Contamination of the Soil Samples
Pooled soil samples after 48 hrs acclimatization was impacted with heavy metals of Fe, Pb, Cd, As, Cu, Zn at concentration of 10mg/g optimized at pH 6.5 as described by Valerro .
2.4. Soil Enzyme Assessment
Soil quality marker enzymes were determined using standard assay protocols, enzyme such as: Lipase, catalase, urease and peroxidase will be assayed.
2.4.1. Lipase
Lipase activity in the soil was determined as described by Elshora et al. .
2.4.2. Catalase
Catalase activity in the soil was determined as described by Eze et al. .
2.4.3. Peroxidase
Peroxidase activity in the soil was determined as described by Eze et al. .
Urease activity in the soil was determined as described by Douglas and Bremner .
2.4.4. Seed Viability Test
This was carried out as described by Merkl et al. using the flotation method.
2.4.5. Cultivation of Seeds of Spinach, Water leaf and Pumpkin
Seeds of Spinach, Water leaf and Pumpkin were cultivated as described by Chukwuma and Adams .
2.5. Determination of the Growth Parameters
2.5.1. Plant Shoot Length Measurement
This will be done as described by Merkl et al. and records were taken every other four (4) days for the respective plants using a meter rule.
2.5.2. Dry Matter Contents
This will be done as described by Merkl et al. using the sensitive weighing balance after drying at constant temperature for days.
2.5.3. Plant Leave Area
Mean area of the plant leaves were determined as described by Chukwu and Adams using the formular 0.5LB where L= length of the leave in cm, B = breath in cm.
Number of leaves per plant stalk was also extrapolated per each plant.
2.5.4. Chlorophyl A and B Determination
This was carried out respectively as described by Merkl et al. absorbance were at 623 and 650nm respectively against acetone solution blank.
3. Results and Discussion
Soil enzyme responses from the agricultural soil impacted with heavy metals of Fe, Pb, Cd, Cu, Zn at concentration of 10mg/g optimized at pH 6.5. Stress marker enzymes of Lipase, catalase, urease and peroxidase assayed showed differential catalytic activity in the presence of the respective heavy metals as shown in figure 1.
Figure 1. Soil enzyme activity in the presence of the heavy metal impacted soil samples.
Analysis of soil enzymes showed the activity of the catalase, peroxidase, lipase and urease, peroxidase and with corresponding OD reading of 0.750, 2.05, 0.22 and 1.704 respectively. There were noticeable increases in the activity of urease and peroxidase while catalase and lipase activity were relatively reduced. Vallero reported the activities of quality marker soil enzymes in the presence of recalcitrant; most constitutive enzymes are said to be mark qualities of soil otherwise House-keeping enzymes whose activities are activated in the presence/influx of recalcitrant to a particular ecological nich(es). Lipases are activated in the presence of triacylglyceride while peroxidase and catalse activity is stimulated in the presence of peroxide and other superoxides; urease activity is activated in the presence of organic matter urea.
Effect of heavy metals on mean shoot length of Amaranthus sp. cultivated in the agricultural soil.
Figures 2, 3 and 4 below shows the differential impact of the heavy metals on development of the cultivated vegetable (Amaranthus sp., Solanum sp and T. Oleifera) in the presence of the heavy metals.
Figure 2. Effect of different trace metals on the mean shoot length of Amaranthus cultivated on agricultural soil Enugu state.
Figure 3. Effect of different trace metals on the mean shoot length of Solanum sp. cultivated on agricultural soil from Enugu state.
Figure 4. Effect of different trace metals on the mean shoot length of T. oceifera cultivated on agricultural soil from Enugu state.
Shoot length as known is the physiology of a plant depicting its growth rate from the soil level. Analysis on the impact of heavy metal pollution on the shoot length of the cultivated vegetables analysed for thirty-one days showed regressive increase in the shoot length of the cultivated vegetables as the period of harvest increases from 0-31 when compared with the control experiment. However Cd and As had the most estimated impact on the vegetables in all the cultivated soils and its impact progresses as the period of harvest increases.
From the results of the respective cultivated vegetables on the soil from Enugu state; there were noticeable non significant difference in soils contaminated with Fe, Cu and Zn and when compared with the control experiment. Mahmood A. and Malik stated that Fe and Cu increases the growth and seedling of their experimented Zea-May and Phaseolus sp. in their study while Pb was a poison to the cultivated crops.
3.1. Effect of Different Trace Metals on the Mean Dry Matter of Amaranthus sp. Cultivated on Agricultural Soil from Enugu State
Figure 5, 6, and 7 below shows the differential impact of the heavy metals on total dry matter contents of the cultivated vegetable (Amaranthus sp., Solanum sp and T. Oleifera) in the presence of the heavy metals.
Figure 5. Effect of different trace metals on the mean dry matter of Amaranthus sp. cultivated on agricultural soil from Enugu state.
3.2. Effect of Different Trace Metals on the Mean Dry Matter of Solanum sp. Cultivated on Agricultural Soil from Enugu State
Figure 6. Effect of different trace metals on the mean dry matter of Solanum sp. cultivated on agricultural soil from Enugu state.
3.3. Effect of Different Trace Metals on the Mean Dry Matter of T.oceifera Cultivated on Agricultural Soil from Enugu State
Figure 7. Effect of different trace metals on the mean dry matter of T. oceifera cultivated on agricultural soil from Enugu state.
Dry matter weight contents of the cultivated vegetables cultivated in the polluted soils were analysed; also the same index was assessed in the vegetables from the un polluted soils. Dry matter contents which reflect the weight content of biological entities devoid of available water (aw). From the figures, there were significant increase in the dry matter contents of the cultivated vegetables in soil polluted with Cu, Fe and Zn respectively. However, dry matter contents were seen progressively low in vegetables cultivated in soils polluted with Cd, As and Pb. When compared with the control experiment, there is a significant decrease in dry matter contents of the vegetables cultivated in soils polluted with Cd, As and Pb respectively however, the dry matter contents were seen higher in vegetables cultivated soils polluted with Fe, Zn and Cu when compared with the control experiment. Thebo et al. (2017) in their experiment on the global, spatially-explicit assessment of irrigated croplands influenced by urban wastewater flows showed a significant impact of divalent Fe on the growth and seedling of Water lilies which reflects positively in its dry matter contents. Merkl et al. exemplified the significant of some fibrous plants like Sativum as phytoremediators in a crude oil impacted soils. They went further to state that there were recorded increase in the growth and productivity of these crops which was aided by bio timely stimulations with minerals like Fe and Zn. Li et al., reported that total dry matter of plants is a quality marker of enriched soil on plant growth as crops cultivated on fertile land grows faster than that of a compromised soil. Chukwu and Adams reported a similar correlation on effect of generator (Exhaust) Fumes on the growth and development of Lycopersicum esculentus (Tomato), in their study, the total dry matter of the tomato plant increases as the cultivation day progresses.
Figure 8. Effect of different trace metals on the total chlorophyll contents of Amaranthus cultivated on agricultural soil from Enugu state.
Effect of different trace metals on the total chlorophyll contents of T.oceifera cultivated on agricultural soil from Enugu state.
Figure 9. Effect of different trace metals on the total chlorophyll contents of T. oceifera cultivated on agricultural soil from Enugu state.
Effect of different trace metals on the total chlorophyll contents of Solanum cultivated on agricultural soil from Enugu state.
Figure 10. Effect of different trace metals on the total chlorophyll contents of Solanum cultivated on agricultural soil from Enugu state.
Total chlorophyl a and b in the selected vegetables showed a correlative increase in chlorophyl a and b in soils contaminated with Zn, Cu and Fe in all the cultivated vegetables: T.oleifera, Amaranthus and Solanum sp respectively.
Recall as described by Valerro that Heavy metals of Zn, Cu and Fe are important biogeochemical metals (ions) which recycles with the olefiers of soils and aquatic bodies and aid in fostering of other nutrient uptake by cultivated plants. He went further to state that they are important metals for pigmentation in any green or other coloured plant(s). There are significant increase in total cholorphyl a and b contents from the results when compared with the control experiment as other soil contaminated with heavy metals such as: Pb, As, Pb repressed the selected vegetables cultivated in the soils. However total chlorophyll a was seen slightly higher than cholophyl b in all the selected vegetables.
4. Conclusion
Agricultural sustainability and revolution stand out as major fulcrum of nations developmental strides. Quest for vegetarian diets is on the increase due to high clinical evidences from animal and other related meal. The statues of these vegetables and alike in the market today remains very obscure. The results from the present study have shown the vulnerability of agricultural soil and cultivated vegetables to effluent from industrial bias sources used for irrigation and its impact on agricultural productivity. These on the long run may endanger the health statues of the peasant farmers who use them for irrigation and the crops cultivated.
Abbreviations

Pb

Lead

Zn

Zinc

Cu

Copper

Pnpp

Paranitrophenyl Palmitate

BDL

Below Detectable Limit

Ethics
Authors declared no ethical issues that may arise after the publication of this manuscript.
Author Contributions
Uchenna Fredrick Anikwe: Conceived and designed the experiments, performed the experiment and processed the data, analyzed the data and wrote the manuscript.
Cyril Onyekachi Edeoga: Co-supervised the research and revised the manuscript.
Emeka Henry Oparaji: Performed the experiment, processed the data and revised the manuscript.
Godwin Ikechukwu Ameh: Analyzed the research design and methodology, interpreted the data.
Funding
This work was solely funded by Anikwe, Uchenna F.
Conflicts of Interest
The authors hereby state that there is no conflict of interest from anybody as regards to this research article.
References
[1] Agency for Toxic Substance Development and Disease Registry (ATSDR), (2010). Documentary on toxicological profile of total petroleum hydrocarbon contaminations. Agency for Toxic Substances and Disease Registry, Division of Toxicoloy and Toxicology Information Branch, Atlanta, Georgia.
[2] Agency for Toxic Substance Development and Disease Registry (ATSDR), (2009). Documentary on toxicological profile of total petroleum hydrocarbon contaminations. Agency for Toxic Substances and Disease Registry, Division of Toxicoloy and Toxicology Information Branch, Atlanta, Georgia.
[3] Agency for Toxic Substance Development and Disease Registry (ATSDR), (2004). Toxicological Profile for Copper. Atlanta, Georgia, United States. US Department of Health and Human Services. Agency for Toxic Substances and Disease Registry.
[4] Agrelli, D., Adamo, P., Cirillo, T., Duri, L. G., Duro, I., Fasano, E., Ottaiano, L., Ruggiero, L., Scognamiglio, G., Fagnano, M (2017). Soil versus plant as indicators of agroecosystem pollution by potentially toxic elements. Journal of Plant Nutrition. Soil Science, 180(6): 705–19.
[5] Ahmad, J. U. and Goni, M. A. (2010). Heavy metal contamination in water, soil, and vegetables of the industrial areas in Dhaka, Bangladesh. Environmental Monitoring and Assessment, 166(1–4): 347–57.
[6] Ahmad, I., Akhtar, J., Zahir, Z. and Jamil, A. (2012). Effect of cadmium on seed germination and seedling growth of four wheat (Triticum aestivum L.) cultivars. Pakistan Journal of Botany, 44(5): 1569–1574.
[7] Akan, J. C., Abdulrahman, F. I., Ogugbuaja, V. O. and Ayodele J. T. (2009). Heavy Metals and Anion Levels in Some Samples of Vegetable Grown Within the Vicinity of Challawa Industrial Area, Kano State, Nigeria. American Journal of Applied Sciences 6 (3): 534-542.
[8] Akinola, M. O., Agbaje, T. A., & Adekola, F. A. (2019). Human health risks assessment of potentially toxic trace metals via consumption of vegetables collected from different wastewater-irrigated agricultural farms of southwestern Nigeria. Environmental Monitoring and Assessment, 191(10), 623.
[9] Aktaruzzaman, M., Fakhruddin, A. N., Chowdhury, M. A., Fardous, Z., Alam, M. K. (2013). Accumulation of heavy metals in soil and their transfer to leafy vegetables in the region of Dhaka Aricha Highway, Savar, Bangladesh. Pakistan Journal of Biological Sciences, 16(7): 332–8.
[10] Alloway, B. J. (2013). Heavy metals in soils: Trace metals and metalloids in soils and their bioavailability (3rd ed.). Springer.
[11] Apeh, S. and Ezugwu, C. N. (2017). Modeling the effect of pollution on Dissolved Oxygen (Do) content of River Benue in Makurdi town. American Journal of Engineering Research (AJER) e-ISSN: 2320-0847 p-ISSN: 2320-0936. 6(6): 204-211.
[12] Arruti, A., Fernández-Olmo, I. and Irabien, A. (2010). Evaluation of the contribution of local sources to trace metals levels in urban PM2.5 and PM10 in the Cantabria region (Northern Spain) Journal of Environmental Monitoring, 12(7): 1451–1458.
[13] Arya, S. and Roy, B. (2011). Manganese induced changes in growth, chlorophyll content and antioxidants activity in seedlings of broad bean (Vicia faba L.). Journal of Environmental Biology, 32(6): 707–711.
[14] Assi, M. A., Hezmee, M. N., Haron, A. W., Sabri, M. Y., Rajion, M. A (2016). The detrimental effects of lead on human and animal health. Veternary World, 9(6): 660–71.
[15] Barnett, H. and Hunters, B. (1972). Illustrated genera of organisms. 3rd edition, Burgess publishing Co., Minneapolis, P. 241.
[16] Basta, N. T., Ryan, J. A. and Chaney, R. L. (2005). Trace element chemistry in residual-treated soil: key concepts and metal bioavailability, Journal of Environmental Quality, 34(1): 49–63.
[17] Bender, D. A., Mayes, P. A., Murray, R. K., Botham, K. M., Kennelly, P. J., Rodwell, V. W. and Weil P. A. (2009). Micronutrients: Vitamins & Minerals". Harper's Illustrated Biochemistry (28th ed.). New York: McGraw-Hill. Archived from the original on 7 September 2010.
[18] Bjuhr, J. (2007). Trace Metals in Soils Irrigated with Waste Water in a Periurban Area Downstream Hanoi City, Vietnam, Seminar Paper, Institutionen for markvetenskap, Sveriges lantbruk- ¨ suniversitet (SLU), Uppsala, Sweden.
[19] Castro-Gonzalez, M and Mendez-Arment, M. (2008). Heavy metals: implications associated with fish consumption Environmental Toxicology and Pharmacology, 26, 263–271.
[20] Centeno, J. A., Tchounwou, P. B., Patlolla, A. K., Mullick, F. G., Murakat, L., Meza, E., Gibb, H., Longfellow, D., Yedjou, C. G. (2005). Environmental pathology and health effects of arsenic poisoning: a critical review. In: Naidu R, Smith E, Smith J, Bhattacharya P, editors. Managing Arsenic In the Environment: From Soil to Human Health. Adelaide, Australia: CSIRO Publishing Corp.
[21] Chen, Z., Ngo, H. and Guo, W. (2013). A critical review on the end uses of recycled water. Critical Review on Environmental Science and Technology, 43: 1446–1516.
[22] Chibuike, G. U. and Obiora, S. C. (2014). Heavy metal polluted soils: effect on plants and bioremediation methods. Appllied and Environmental Soil Science.
[23] Chikere, C., Okpokwasili, G. and Chikere, B. (2009). Bacterial diversity in typical crude oil polluted soil undergoing bioremediation. African Journal of Biotechnology, 8: 2535–2540.
[24] Chukwu, M. and Adams, E. (2016). Effect of Generator (Exhaust) Fumes on the Growth and Development of Lycopersicum esculentus (Tomato). Journal of Applied Environmental Science and Management, 20 (2) 335– 340.
[25] Clarkson, T. W., Magos, L. and Myers, G. J. (2003). The toxicology of mercury: current exposures and clinical manifestations. New England Journal of Medicine, 349: 1731–1737.
[26] Das, S., Jean, J. S., Yang, H. J., & Liu, C. C. (2019). Metal toxicity to plants: From mechanisms to remediation. Ecotoxicology and Environmental Safety, 183, 109520.
[27] Douglas, D. and Bremner, E. (1971). A rapid method of evaluating different compounds as inhibitors of urease activity in soil. Soil Biology and Biochemistry, 3: 309-315.
[28] Ejedegba O., Onyeneke, E. and Oviasogie, P. (2007). Characterisation of lipase isolated from coconut seed under different nutrient conditions. African Journal of Biotechnology, 6: 723-727.
[29] El-Shora, H., Ibrahim, M. and Elmekabaty, M. (2017). Immobilization and thermostability of lipase from Jatropha seed. Microbiology Research Journal, International, 21(2): 1-11.
[30] Eze, S. O. O., Chilaka, F. C., Nwanguma, B. C. (2012) Studies on Thermodynamics and Kinetics of Thermo-Inactivation of Some Quality-Related Enzymes in White Yam (Dioscorea rotundata). Journal of Thermodynamic and Catalysis, 1: 104.
[31] Ezenwelu, C., Aribodor, O., Ezeonyejiaku, C., Okafor, S. and Oparaji, E. (2022). Assessment of physicochemical properties and microbial loading index of soil samples from mgbuka market, Anambra state. Journal of Environmental Pollution and Management, 12: 134-176.
[32] Ezeonu, M., Okafor, J. and Ogbonna, J. (2013). Laboratory Exercises in Microbiology. 1st Edn. Ephrata Publishing and Printing Company, Nsukka. Pp 100-117.
[33] Gautam, P. K., Gautam, R. K., Chattopadhyaya, M. C., Banerjee, S. and Pandey J. D (2016). Heavy metals in the environment: fate, transport, toxicity and remediation technologies Thermodynamic profiling of pollutants View project Materials for Solid oxide fuel cells View project Heavy Metals in the Environment: Fate Transport, Toxicity and Rem.
[34] Gertler, C., Gerdts, G., Timmis, K., Yakimov, M. and Golyshin, P. (2009). Populations of heavy fuel oil-degrading marine microbial community in presence of sorbent materials. Journal of Applied Microbiology, 107: 590–605.
[35] Haluk, E., Khawar. S. S., Julia. M., Tim. C., Ricardo, C. (2012). Kinetic and thermodynamic characterization of the functional properties of a hybrid versatile peroxidase using isothermal titration calorimetry: Insight into manganese peroxidase activation and lignin peroxidase inhibition. Biochimie, 94: 1221-1231.
[36] Hao, H., Zhong, R., Miao, Y., Wang, Y. and Liu, C. (2012). The intercropping influence on heavy metal uptake for hyperaccumulators Proceedings of the Proceedings - International Conference on Biomedical Engineering and Biotechnology, iCBEB; IEEE, pp. 1826-1828.
[37] Ibrahim, H. Y and Omotesho, O. A (2013). Determinant of technical efficiency in vegetable production under Fadama in northern Guinea savannah, Nigeria. International Journal of Agricultural Technology. 9(6): 1367-1379.
[38] Igwe, J. C and Abia, A. A (2003). “Maize Cob and Husk as Adsorbents fot removal of Cd, Pb and Zn ions from wastewater,” The Physical Science, vol. 2, pp. 83-94.
[39] Iyama, W. A. and Edori, O. S (2020). Assessment of levels and safe factor index of heavy metals in soils around Diobu, Port Harcourt, Nigeria. International Journal of Advanced Research in Chemical Science, 7(8): 1-15.
[40] Jaishankar, M., Tseten, T., Anbalagan, N., Mathew, B. B., Beeregowda, K. N (2014). Toxicity, mechanism and health effects of some heavy metals. Interdisciplinary Toxicology, 7(2): 60–72.
[41] Jones, L. H. P. and Jarvis, S. C. (1981). The fate of heavy metals, in The Chemistry of Soil Processes, D. J. Green and M. H. B. Hayes, Eds., John Wiley and Sons, New York, p. 593.
[42] Jyotish Katare, Mohnish Pichhode and Kumar Nikhil (2015). Growth of Terminalia bellirica [(gaertn.) roxb.] on the malanjkhand copper mine overburden dump spoil material. International Journal of Research – GRANTHAALAYAH, 3: 14-24.
[43] Kabata-Pendias, A. (2010). Trace elements in soils and plants (4th ed.). CRC Press.
[44] Ladislao, B. (2009) Polycyclic Aromatic Hydrocarbons, Polycholirnated Biphenyls, Phthalates and Organotins in Northern Atlantic Spain’s Coastal Marine Sediments. Journal of environmental monitoring, 11: 85-91.
[45] Lasat, M. M. (2000). Phytoextraction of metals from contaminated soil: a review of plant/soil/metal interaction and assessment of pertinent agronomic issues, Journal of Hazardous Substances Research, 2: 1–25.
[46] Leenders M., et al (2014) Fruit and vegetable intake and cause-specific mortality in the EPIC study. European Journal of Epidemiology, 29(9): 639-52.
[47] Li, N. Y., Li, Z. A., Zhuang, P., Zou, B., McBride, M. (2009). Cadmium uptake from soil by maize with intercrops. Water. Air and Soil Pollution. 199: 45-56.
[48] Li, J., Liu, G., Yin, L., Xue, J., Qi, H. and Li, Y. (2013). Distribution characteristics of polycyclic aromatic hydrocarbons in sediments and biota from Zha Long Wet Land, China. Environmental Monitoring Assessment, 185: 3163–3171.
[49] Li, R., Wu, H., DIng, J., Fu, W., Gan, L., Li, Y (2017). Mercury pollution in vegetables, grains and soils from areas surrounding coal-fired power plants. Scientific Report, 7: 46545.
[50] Liu, T., Liu, Y., Cui, Y., & Song, Z. (2020). Uptake, accumulation, and toxicity of heavy metals in crops: A review. Environmental Science and Pollution Research, 27(27), 33494-33507.
[51] Mahmood, A. and Malik, R. (2014). Human health risk assessment of heavy metals via consumption of contaminated vegetables collected from different irrigation sources in Lahore, Pakistan. Arabian Journal of Chemistry, 7: 91–99.
[52] Mattigod, S. V. and Page, A. L. (1983). Assessment of metal pollution in soil, in Applied Environmental Geochemistry, Academic Press, London, UK, pp. 355–394.
[53] McLaren, R. G., Clucas, L. M. and Taylor, M. D. (2004). Leaching of macronutrients and metals from undisturbed soils treated with metal-spiked sewage sludge, Australian Journal of Soil Research, 43(2): 159–170.
[54] McLaughlin, M. J., Hamon, R. E., McLaren, R. G., Speir, T. W. and Rogers, S. L. (2000) Review: a bioavailability-based rationale for controlling metal and 61 metalloid contamination of agricultural land in Australia and New Zealand, Australian Journal of Soil Research, 38(6): 1037–1086.
[55] Mendez, M. O., & Maier, R. M. (2008). Phytoremediation of mine tailings in temperate and arid environments. Reviews in Environmental Science and Bio/Technology, 7(1), 47-59.
[56] Mensink, G. D. M, Truthmann, J. and Rabenberg M, et al. (2013). Fruit and Vegetables intake in Germany. Bundesgesundheitsbl, 56: 779–785.
[57] Merkl, N., Schultze-Kraft, R. and Infante, C. (2004). Phytoremediation in the Tropics. The Effect of Crude Oil on the Growth of Tropical Plants. Bioremediation Journal, 8: 177-184.
[58] Mirzabeygi, M., Abbasnia, A., Yunesian, M., Nodehi, R. N., Yousefi, N., Hadi, M. and Mahvi, A. H (2017). Heavy metal contamination and health risk assessment in drinking water of Sistan and Baluchistan, Southeastern Iran. Hum Ecological Risk Assessment 23(8): 1893–905.
[59] Mohnish Pichhode, Kumar Nikhil (2015). Effect of copper dust on photosynthesis pigments concentrations in plants species. International Journal of Engineering Research and Management, 2: 63-66.
[60] Morris, R. (1952). Determination of Iron in water in presence of heavy metals. Analytical Chemistry, 24(8): 1376-1378.
[61] Nogale, B., Lanfranconi, M., Pina-Villalonga, J. and Bosch, R. (2011). Anthropogenic Perturbation in Marine Microbial Communities. FEMS microbial rev., 35: 275-298.
[62] Oguh, C. E., Ubani, C. S., Osuji, C. A. and Ugwu, C. V (2019). Heavy metal risk assessment on the consumption of Talinum triangulare grown on sewage dump site in University of Nigeria, Nsukka. Journal of Research in Environmental Science and Toxicology. 8(2) pp. 104-112.
[63] Nriagu, J. O. (1996). A history of global metal pollution. Science of the Total Environment, 177(1-3), 3-11.
[64] Nworie, O., Okoro, V., & Nworie, J. (2020). Sustainable agriculture and food security in Nigeria: The need for integration of research results and policy implementation. In Sustainable Development and Biodiversity (pp. 267-283). Springer.
[65] Serpe, F., Esposito, M., Gallo, P., Salini, M., Maglio, P., Hauber, T. and Serpe, L. (2010). Determination of Heavy Metals, Polycyclic Aromatic Hydrocarbons and Polychlorinated Biphenyls in MytilusGalloprovincialis from Campania Coasts, Italy. Fresen environmental bulletin, 19: 2292-2296.
[66] Valerro D. (2010). Environmental biotechnology: A Biosystems approach. 4th edition. Pp. 1245-1453.
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    Anikwe, U. F., Ameh, G. I., Edeoga, C. O., Oparaji, E. H. (2024). Soil Enzyme Responses and Crop Productivity Indices Assessment in Agricultural Soil Impacted with Heavy Metals. American Journal of Chemical and Biochemical Engineering, 8(2), 34-44. https://doi.org/10.11648/j.ajcbe.20240802.11

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    Anikwe, U. F.; Ameh, G. I.; Edeoga, C. O.; Oparaji, E. H. Soil Enzyme Responses and Crop Productivity Indices Assessment in Agricultural Soil Impacted with Heavy Metals. Am. J. Chem. Biochem. Eng. 2024, 8(2), 34-44. doi: 10.11648/j.ajcbe.20240802.11

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    AMA Style

    Anikwe UF, Ameh GI, Edeoga CO, Oparaji EH. Soil Enzyme Responses and Crop Productivity Indices Assessment in Agricultural Soil Impacted with Heavy Metals. Am J Chem Biochem Eng. 2024;8(2):34-44. doi: 10.11648/j.ajcbe.20240802.11

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  • @article{10.11648/j.ajcbe.20240802.11,
      author = {Uchenna Fredrick Anikwe and Godwin Ikechukwu Ameh and Cyril Onyekachi Edeoga and Emeka Henry Oparaji},
      title = {Soil Enzyme Responses and Crop Productivity Indices Assessment in Agricultural Soil Impacted with Heavy Metals
    },
      journal = {American Journal of Chemical and Biochemical Engineering},
      volume = {8},
      number = {2},
      pages = {34-44},
      doi = {10.11648/j.ajcbe.20240802.11},
      url = {https://doi.org/10.11648/j.ajcbe.20240802.11},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ajcbe.20240802.11},
      abstract = {The present study assessed the productivity of cultivated garden vegetable among other ecological assessments in soil samples impacted with heavy metals. Assay of soil enzyme responses showed the activity of: catalase, peroxidase, lipase and ureasewith corresponding OD reading of 0.750, 2.05, 0.22 and 1.704 respectively. There were noticeable increases in the activity of ureaseandperoxidasewhilecatalaseandlipaseactivitywererelativelylowinthesampledsoil. Out of the 321g of the vegetable seedstested for viability, 45% representing 144.45g was used for the planting and further experiment. After three days of cultivation, germination process was recorded faster in the T. oleifera potted ridge while Amaranthus and Solanum sp seed took 3-4 day for break full dormancy. Determination of total chlorophyll a and b in the selected vegetables showed a correlative increase in chlorophyll a and b in soils contaminated with Zn, Cu and Fe in all the cultivated vegetables: T. oleifera, Amaranthus and Solanum sp, respectively. There are significant increase in total cholorphyl a (0.9mg/g) and b (0.8mg/g) contents from the results when compared with the control experiment as other soil contaminated with heavy metals such as: Pb, and As repressed the selected vegetables cultivated in the soil samples. However total chlorophyll a was seems lightly higher than cholophyl b in all the selected vegetable cultivated in soil. Analysis on the impact of heavy metals on the shootlength of the cultivated vegetables analysed for thirty-one days showed regressive increase in the shootlength of the cultivated vegetables as the period of harvest increases from 0-31 when compared with the control experiment. However Cd and As had the most estimated impact on the vegetables in all the cultivated soils and its impact progresses as the period of harvest increases. Dry matter weight contents of the cultivated vegetables cultivated in the polluted soils were analysed; also the same index was assessed in the vegetables from the unpolluted soils. There was a significant increase in the dry matter contents of the cultivated vegetables in soil polluted with Cu, Fe and Zn respectively. However, dry matter contents were seen progressively low in vegetables cultivated in soils polluted with Cd, As and Pb. When compared with the control experiment. The results from the present study have shown the vulnerability of agricultural soil and cultivated vegetables to effluent from industrial bias sources used for irrigation and its impact on agricultural productivity.
    },
     year = {2024}
    }
    

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  • TY  - JOUR
    T1  - Soil Enzyme Responses and Crop Productivity Indices Assessment in Agricultural Soil Impacted with Heavy Metals
    
    AU  - Uchenna Fredrick Anikwe
    AU  - Godwin Ikechukwu Ameh
    AU  - Cyril Onyekachi Edeoga
    AU  - Emeka Henry Oparaji
    Y1  - 2024/09/29
    PY  - 2024
    N1  - https://doi.org/10.11648/j.ajcbe.20240802.11
    DO  - 10.11648/j.ajcbe.20240802.11
    T2  - American Journal of Chemical and Biochemical Engineering
    JF  - American Journal of Chemical and Biochemical Engineering
    JO  - American Journal of Chemical and Biochemical Engineering
    SP  - 34
    EP  - 44
    PB  - Science Publishing Group
    SN  - 2639-9989
    UR  - https://doi.org/10.11648/j.ajcbe.20240802.11
    AB  - The present study assessed the productivity of cultivated garden vegetable among other ecological assessments in soil samples impacted with heavy metals. Assay of soil enzyme responses showed the activity of: catalase, peroxidase, lipase and ureasewith corresponding OD reading of 0.750, 2.05, 0.22 and 1.704 respectively. There were noticeable increases in the activity of ureaseandperoxidasewhilecatalaseandlipaseactivitywererelativelylowinthesampledsoil. Out of the 321g of the vegetable seedstested for viability, 45% representing 144.45g was used for the planting and further experiment. After three days of cultivation, germination process was recorded faster in the T. oleifera potted ridge while Amaranthus and Solanum sp seed took 3-4 day for break full dormancy. Determination of total chlorophyll a and b in the selected vegetables showed a correlative increase in chlorophyll a and b in soils contaminated with Zn, Cu and Fe in all the cultivated vegetables: T. oleifera, Amaranthus and Solanum sp, respectively. There are significant increase in total cholorphyl a (0.9mg/g) and b (0.8mg/g) contents from the results when compared with the control experiment as other soil contaminated with heavy metals such as: Pb, and As repressed the selected vegetables cultivated in the soil samples. However total chlorophyll a was seems lightly higher than cholophyl b in all the selected vegetable cultivated in soil. Analysis on the impact of heavy metals on the shootlength of the cultivated vegetables analysed for thirty-one days showed regressive increase in the shootlength of the cultivated vegetables as the period of harvest increases from 0-31 when compared with the control experiment. However Cd and As had the most estimated impact on the vegetables in all the cultivated soils and its impact progresses as the period of harvest increases. Dry matter weight contents of the cultivated vegetables cultivated in the polluted soils were analysed; also the same index was assessed in the vegetables from the unpolluted soils. There was a significant increase in the dry matter contents of the cultivated vegetables in soil polluted with Cu, Fe and Zn respectively. However, dry matter contents were seen progressively low in vegetables cultivated in soils polluted with Cd, As and Pb. When compared with the control experiment. The results from the present study have shown the vulnerability of agricultural soil and cultivated vegetables to effluent from industrial bias sources used for irrigation and its impact on agricultural productivity.
    
    VL  - 8
    IS  - 2
    ER  - 

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Author Information
  • Department of Applied Biology, Enugu State University of Science and Technology, Enugu, Nigeria

  • Department of Applied Biology, Enugu State University of Science and Technology, Enugu, Nigeria

  • Department of Applied Biology, Enugu State University of Science and Technology, Enugu, Nigeria

  • Department of Biochemistry, University of Nigeria, Nsukka, Nigeria

  • Abstract
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    1. 1. Introduction
    2. 2. Materials and Methods
    3. 3. Results and Discussion
    4. 4. Conclusion
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