Introduction
Tea is the most popular beverages and an important plantation crop cultivated in India along with many other areas of the world (Nath)1. It is not only a much liked beverage of the people in the country but also fetches a good amount of foreign exchange (Karmakar and Banerjee)2. Tea is produced from the leaves of tea plant scientifically called Camellia sinensis (L.) O. Kuntze. Tea plants are leafy perennial trees planted and pruned to desirable height with an objective of recurring harvest. The quality of tea leaf used for manufacturing is highly influenced by soil nutrients and tea clone. Concentration of nutrients in tea leaf is related with the soil environment (Özyazici et al.,3). Mineral content of harvested tea depend on the soil properties on which it is grown along with its agronomic practice (Kalita and Mahanta4). So, the contents of nutrient element of tea plant are related with soil environments.
In India, the tea plant was discovered growing wild in upper Assam (India) in 1821 (Roy)5. In West Bengal, the first tea garden was established in 1857 at Darjeeling, thereafter tea plantations started extending down to sub Himalayan Terai region from 1862 and Dooars from 1874 (Joseph)6. So, tea plantations of Terai and Dooars are around 150 years old. Being a plantation crop, the land is utilized for monoculture of tea. More than a century long exploitation of soil under tea cultivation in Terai and Dooars has led to degradation of soil fertility. Maintenance of soil nutritional quality is a massive economic burden to the local tea growers in view of a huge amount of chemical inputs sharing a good proportion of manufacturing cost every recurring year. In addition injudicious application of chemical fertilizers in large quantities without having a fair qualitative knowledge of tea plantation soil results in destabilization or decline of yields. Adequate soil testing can regulate the quantity of fertilizer loads providing a clear idea of how much exactly chemical inputs are required, and thus can restrict imprudent usage of excess soil nourishment agents.
Soil being one of the most important factors for quality tea produce has not been investigated to a great extent. There are some scattered literature on soil nutrient status of Mengding Mountain, China (Zheng et al.,7), Fujian Province, China (Ping)8, Black sea region, Turkey3, Dibrugarh and Sivasagar district of Assam, India1. But, soil nutrient status of Terai and Dooars region are extremely lacking. So the present study was conducted to determine the pH, total nitrogen, phosphorus and potassium in tea plantations of Terai and Dooars region of sub Himalayan West Bengal, India.
Materials and Methods
Study Area
Terai (plains of Darjeeling district) and Dooars (plains of Jalpaiguri and Alipurduar districts) regions are located inplains of sub Himalayan West Bengal, India. These two regions have cool winter with warm and humid summer. Rainfall is common almost throughout the year with heavy downpours during the rainy season. Six tea plantations of Terai and nine tea plantations of Dooars region were considered for the present study of soil nutritional status.
Soil Sampling
In our study area, a total number of 126 soil samples were collected by means of a screw type auger of which 54 samples were from Terai and 72 samples were from Dooars region. Each sample was gathered by mixing five presamples collected from the corners of an imaginary square of ten metres side and from its diagonal bisector. About five hundred grams of soil samples were brought to laboratory in airtight zipper bags for downstream analysis. Soil samplings were performed early in the morning before application of fertilizers. Topsoil (0-15 cm) and sub soil (15-30 cm) were dug under the canopies of tea bushes.
Preparation of Soil Samples for Analysis
The collected soil samples were completely air dried. Debris from the samples like roots, pebbles etc were removed by hand. The clean air dried samples were passed through 2mm sieve and crushed with mortar and pestle. For organic carbon determination, the samples were further passed through final mesh sieve (0.5mm).
Estimation of Soil pH
pH of soil samples were measured on precalibrated pH meter following protocol of Baruah and Barthakur9.
Determination of Soil Organic Carbon Content
Quantification of soil organic carbon was conducted by Chromic acid method proposed by Walkley and Black10.
Determination of Total Soil Nitrogen, Available Phosphorus and Potassium
Total soil was determined by Kjeldhal method (Jackson)11. Estimation of phosphorus as phosphate and potassium as potash requires diacid digestion of soil. One gram sample was subjected to diacid digestion9. Available phosphorus in the digested sample solution in form of phosphate was conducted by the protocol developed by Bray and Kurtz12. Determination of available potassium form of Poatash was conducted by the protocol developed by Chapman and Pratt13.
Nutritional Index
Nutritional index for soil organic carbon, total nitrogen, available phosphorus (as P2O5) and potassium (as K2O) were calculated to determine the soil nutritional status of Terai and Dooars region. Nutritional index was calculated following Sharma, et al.,14.
Statistical Analysis
Descriptive statistics in the form of mean, minimum, maximum value and standard deviation (SD) were analysed using SPSS software and MS Excel.
Result and Discussion
Soil pH
Soil reaction is measured by pH of a suspension of soil in water. In tea plantations the pH within the range of 4.5-5.5 has been recommended (https://www.tocklai.org/activities/tea-cultivation/). The pH of the soil samples collected across the study area was variable (table I). In the top soil of Terai region soil pH ranged 4-5.30 with an average of 4.42; while in the sub soil it ranged 3.86-5.18 with an average of 4.47. In the top soil of Dooars region it ranged 4.77-4.90 with an average of 4.84; while in the sub soil of it ranged 4.91-4.96 with an average of 4.93. The soil pH of Dooars region was found to be more than the Terai region. The influence of dolomite brought down by rivers from neighbouring Bhutan may be the main reason behind such pH. In both Terai and Dooars tea plantations, pH of the subsoil was found to be more than top soil. In top soil of Terai region the pH was lower than the recommended pH but pH of the sub soil was within the range. In the Dooars region the pH of both top and sub soil was within the recommended range.
Table 1: pH, Organic Carbon, Total Nitrogen, Phosphorus and Potassium of Soil Samples
Soil parameter | Region | Top soil | Sub soil | ||
Average | Range | Average | Range | ||
pH (4.5-5.5)* | Terai | 4.42±0.25 | 4-5.30 | 4.47±0.26 | 3.86-5.18 |
Dooars | 4.84±0.43 | 4.77-4.9 | 4.93±0.42 | 4.91-4.96 | |
Organic carbon (1.0-2.0%)* | Terai | 2.18±1.04 | 0.46-4.46 | 2.09±1.21 | 0.41-5.96 |
Dooars | 1.7±0.71 | 1.6-1.8 | 1.42±1.22 | 1.33-1.48 | |
Total Nitrogen (0.1-2.0%)* | Terai | 0.15±0.05 | 0.01-0.31 | 0.13±0.04 | 0.04-0.25 |
Dooars | 0.14±0.03 | 0.13-0.14 | 0.12±0.04 | 0.12-0.12 | |
Phosphate as P2O5 (10-20 ppm)* | Terai | 24.31±26.75 | 1-140 | 9.7 ±13.58 | 1-80 |
Dooars | 59.98±59.87 | 58.41-60.95 | 41.05 ±40.13 | 39.62-43.91 | |
Potassium as K2O (60-80 ppm)* | Terai | 207 ±6 | 80-410 | 175 ±58 | 70-331 |
Dooars | 153 ±28 | 145-161 | 150±24 | 149-152 |
*=standard as recommended by Tea Board of India
Percentages of soil samples with low, normal and high pH are depicted in table II. 79% of the collected soil samples from Terai and 84.5% samples from Dooars region were found to have normal pH. Rest samples showed either low or high pH. The sub-Himalayan Terai region comprises of the plains of Darjeeling district. In this region the soils are mostly sandy, highly acidic, heavily leached and poor in plant nutrients (Bhattacharya)15. In the Dooars region, rivers flowing from neighboring Bhutan carry a large quantity of dolomite dust along with silt that sediment on the soil of tea plantations during floods occurring in the rainy season. So this might be a reason for well maintenance of soil pH of this region by natural means.
Table 2: Percentages (%) of Soil Samples with Low, Normal and High pH
Soil parameter | Soil layer | Terai | Dooars | ||||
Low | Normal | High | Low | Normal | High | ||
pH (4.5-5.5)* | Top | 15 | 77 | 7 | 11 | 83 | 5.5 |
Sub | 9 | 81 | 9 | 7 | 86 | 7 | |
Organic carbon (1-2%)* | Top | 5.5 | 48 | 46 | 16 | 46 | 37.5 |
Sub | 13 | 46 | 40 | 28 | 53 | 19 | |
Total Nitrogen (0.1-2.0%)* | Top | 11 | 88 | 00 | 14 | 86 | 00 |
Sub | 13 | 86 | 00 | 28 | 72 | 00 | |
Phoshorus as P2O5 (10-20ppm)* | Top | 39 | 13 | 48 | 4 | 8 | 87.5 |
Sub | 72 | 13 | 14 | 8 | 16 | 75 | |
Potassium as K2O (60-80ppm)* | Top | 0 | 1.8 | 98 | 0 | 0 | 100 |
Sub | 0 | 4 | 96 | 0 | 0 | 100 |
*=standard as recommended by Tea Board of India
Organic Carbon
Soil organic matter is the summation of non mineral matter present in soil, and a series of product from decayed plant and animal tissue. The role of soil organic matter for fertility and physical conditions of soil, are well accepted. Decomposition of organic matter by micro-organisms in soil and stabilization of soil structure plays an important role in nutrient cycling (Dick et al.,16; Quilchano and Maranon17; Singh et al.,18).
A rich tea garden soil has 2% organic carbon while below 1% need attention (https://www.tocklai.org/activities/tea-cultivation/). Organic carbon content of the soil of Terai and Dooars region are within the Tea Board of India (1-2%) recommended range or slightly high (table I). The percentage of organic carbon content both top (2.18%) and sub (2.09%) soil of Terai region was above the Tea Board of India recommended standard. But, the quantity of organic carbon content in both top (1.7%) and sub (1.42%) soil of Dooars region was within the recommended range.
Percentage of soil samples with low, normal and high organic carbon content are depicted in table II. Maximum number of collected soil samples was found to have normal organic carbon. A few samples showed low organic carbon. In Terai region 46.29 and 40.74% of samples showed high organic carbon in top and sub soil respectively. 37.5 and 19.44 percentage of samples of Dooars region showed high organic carbon in top and sub soil respectively. Soil biochemical activities have been found to be very responsive in organic cultivation17, Miller and Dick20: Bergstrom et al., 21. The application of chemical fertilizers to ensure fertility of soil and crop productivity may negatively act on the complex mechanism of biogeochemical cycle (Tilman et al., 22; Adesmoyce and Kloepper23).
Total Nitrogen, Available Phosphorus and Potassium
Nitrogen (N) is one of the most important constituent of plant parts and plays a crucial part in plant physiology. Total nitrogen content of tea plantation soil of Terai and Dooars regions was normal (table I). Total nitrogen content estimated in both top (0.152%) and sub (0.139%) soil of Terai region, and total nitrogen content of both top (0.141%) and sub (0.125%) soil in Dooars region was within the range (0.1-2.0%) recommended by Tea Board of India. Soil samples with low, normal and high total nitrogen are depicted in table II. 88% of the tested soil samples of Terai and 79% of samples from Dooars showed normal total nitrogen percentage. 12% and 21% of samples from Terai and Dooars region showed low total nitrogen content. There is a positive correlation (0.9233) between organic carbon and nitrogen percentage in soil. Chief reason for low nitrogen content in some region may be due to low use efficiency of the externally applied fertilizers by plants as well as their long term application. Since 1980s, the use of nitrogen in tea plantations has been increasing rapidly; though several researchers are being involved in the study on tea, research work on mineral nutrition is rare (Luczaj and Skrzydlewska)24.
Phosphorus (P) is also an essential macronutrient, after nitrogen (N) for plants and its deficiency is the most limiting factor for growth and development of plants (Kumar et al.,25). Application of phosphorus fertilizer is usually recommended for enhancing soil phosphate availability (Vance et al.,26: Lamberset al.,27). However, only less than 20% of phosphorus can be utilized by the plants and the 80-90% of applied phosphorus is fixed into the soil27. Due to the limited availability and resources of phosphate fertilizers and their effects on environment, their extensive use can be a threat to the agriculture26-27). Available phosphorus in form of phosphate of tea plantation soil of Terai and Dooars regions are extremely variable (table I). In Terai region the phosphate content of top soil (24.314ppm) was found to be above the range but the sub soil (9.703ppm) was below the range (10-20ppm) recommended by Tea Board of India. In Dooars region both top (59.986ppm) and sub (41.055ppm) soil was found to contain phosphate above the range recommended by Tea Board of India. Percentages of soil samples with low, normal and high phosphate are depicted in table II. The soil samples collected from different sites showed extremely variable results. Top and subsoil samples collected from Dooars region showed high percentage of phosphate in soil. While, sub soil of about 75% soil samples of Terai region has low phosphate content. The probable reason is, soil of Terai region expresses different texture where it is mainly sandy compared to Dooars.
The tea growing areas generally have moderately to highly acidic soil and it is well established that under the acidic or calcareous soil large amount of phosphorus is fixed (Gyaneswaret al., 28). The problem of phosphorus deficiency is of particular concern for acid soil like tea garden soil, as tea prefers a low pH (4.5-5.5) soil (Zoysaet al.,29); which cause unavailability of phosphorus due to binding to soil mineral surfaces and fixation into organic forms27; (Kochianet al.,30). Additionally, when concentration of phosphate in soil exceeds the natural soil-phosphate holding capacity, phosphate can be carried downward, or leached; commonly referred to as phosphate leaching (Bolan et al.,31). The subsoil of both Terai and Dooars have less pH than the top soil, so the phosphate binding capacity of the top soil is quite good and there is no concern about phosphate leaching. Potassium is required in large amounts since it is involved in almost all biological reactions. After nitrogen, potassium is the second major nutrients required for tea cultivation and constitute 1.5-2% of tea leaf dry matter (Verma32&33 & Xunet al., 34). Potassium deficiency occurs in the tea plantation mainly due to excessive leaching as a consequence of higher precipitation and more demands by plants as well33&34. Available potassium in form of potash of tea plantation soil of Terai and Dooars regions is high (table I). In Terai region the potash content of both top soil (207.037ppm) and sub soil (175.851ppm) was far above the range recommended by Tea Board of India (10-20ppm). In Dooars region too both top (153.8479ppm) and sub (150.694ppm) soil was found to contain potash well above the range recommended. Percentages of soil samples with low, normal and high potash are depicted in table II. Leaving a few illustrations all samples of Terai region exhibited high potash content while all soil samples collected from Dooars region too showed high potash content.
Nutritional Index
Nutritional index determines the overall nutritional quality of soil. The overall nutritional quality of Terai and Dooars tea plantation soil were medium to high except some isolated cases. Nutritional index of organic carbon, total Nitrogen, available phosphate and potash in soil samples of Terai and Dooars were determined and represented as table III. In the soil samples of Terai region organic carbon content of top soil and available potash of both top and sub soil showed high nutritional index. Organic carbon content of sub soil and available phosphate content of top soil showed medium nutritional index. Only available phosphate content of sub soil showed low nutritional index. Both Terai and Dooars region nutritional index of Nitrogen was at medium range. In Dooars region nutritional index of both top and sub soil in terms of available phosphate and potash were high.
Table 3: Nutritional Index (NI) of Tea Plantation Soil of Sub Himalayan West Bengal
Soil parameter | Terai | Dooars | |||||||
Soil layer | Low
<1.67 |
Medium
1.67-2.33 |
High
>2.33 |
NI | Low
<1.67 |
Medium
1.67-2.33 |
High
>2.33 |
NI | |
Organic Carbon | Top | 3 | 26 | 25 | 2.40 | 12 | 33 | 27 | 2.20 |
Sub | 7 | 25 | 22 | 2.27 | 20 | 38 | 14 | 1.91 | |
Total Nitrogen | Top | 6 | 48 | 0 | 1.88 | 10 | 62 | 0 | 1.86 |
Sub | 7 | 47 | 0 | 1.87 | 20 | 52 | 0 | 1.72 | |
Phosphorus as P2O5 | Top | 21 | 7 | 26 | 2.09 | 3 | 6 | 63 | 2.83 |
Sub | 39 | 7 | 8 | 1.42 | 6 | 12 | 54 | 2.66 | |
Potassium as K2O | Top | 0 | 1 | 53 | 2.98 | 0 | 0 | 72 | 3 |
Sub | 0 | 2 | 52 | 2.96 | 0 | 0 | 72 | 3 |
Conclusion
The majestic beauty of sub-Himalayan West Bengal is for its landscape, forests and Tea gardens. The economy of this region is dependent on three T’s- Tea, Timber and Tourism. The tea gardens spread over every corner of this region practice monoculture of tea which has partially declined the soil nutritional quality thereby adversely affecting quality of manufactured tea. Moreover change in rainfall pattern and deteriorated water-holding capacity resulted in loss of soil biota and acidification. All these deteriorative features reduce plant root growth and plant health. The experimental findings too clearly depicts that proper pedological analysis can restrict use of excess chemical inputs and ascertain the soil nutrient level predicting which sort of nourishment elements are actually required for the benefit of the plantation providing a fiscal advantage to the tea growers. Thus, scientific fertility replenishment initiative must be implemented on an emergency basis to save tea plantations and boost the economy of the region.
Acknowledgement
The authors would like to acknowledge the Tea plantations for providing soil samples for analysis.
Funding Source
The corresponding author would like to acknowledge that the present study was partially supported by research fund (1954/R-2019) received by him.
Conflict of Interest
There is no conflict of interest.
References
- Nath, T.N. The status of micronutrients (Mn, Fe, Cu, Zn) in tea plantations in Dibrugarh district of Assam, India. International Research Journal of Environment Sciences 2013; 2(6), 25-30.
- Karmakar, K.G., and Banerjee, G.D. (2005). The tea industry in India: a survey; Mumbai: National Bank for Agriculture and Rural Development.
- Özyazıcı, M.A., Özyazıcı, G., and Dengiz, O. Determination of micronutrients in tea plantations in the eastern Black Sea Region, Turkey. African Journal of Agricultural Research 2011;6(22), 5174-5180.
- Kalita, J.N., and Mahanta, P.K. Analysis of mineral composition of some Assam and Darjeeling black teas. Journal of the Science of Food and Agriculture 1993;62(2), 105-109.
CrossRef - Roy, S. Historical review of growth of tea industries in India: a study of Assam Tea. In International Conference on Social Science and Humanity 2011;1, 116-170.
- Joseph, M. (2002). Problems and prospects of tea plantation industry in Kerala.
- Zheng, Z., He, X., and Li, T. Status and evaluation of the soil nutrients in tea plantation. Procedia Environmental Sciences2012;12, 45-51.
CrossRef - Ping, X., Liyun, Y., Moucheng, L., and Fei, P. Soil Characteristics and Nutrients in Different Tea Garden Types in Fujian Province, China. Journal of resources and ecology 2014; 5(4), 356-364.
CrossRef - Baruah, T.C., and Barthakur, H.P. (1997). A Textook of Soil Analysis. Vikash Publishing House Pvt. Ltd., New Delhi.
- Walkey, A., and Black, C.A. (1974). Critical examination of rapid method of determining organic carbon in soil. Soil Science 1974;63, 251-164.
CrossRef - Jackson, M.L. (1973). Soil Chemical Analysis. Prentice Hall of India Pvt. Ltd., New Delhi, 498.
- Bray, R.H., and Kurtz, L.T. Determination of total, organic, and available forms of phosphorus in soils. Soil science 1945; 59(1), 39-46.
CrossRef - Chapman, H.D., and Pratt, P.F. (1961). Ammonium vandate-molybdate method for determination of phosphorus. Methods of analysis for soils, plants and water, California University, Agriculture Division, 184-203.
- Sharma, S., Choudhury, P., & Chetryd, N. Status of soil nutrients and fertility of four land use system in Raid-Marwet region, Ri-Bhoi district of Meghalaya, India. Journal of Global Biosciences 2016;5(6), 4178-4187.
- Bhattacharya, M. (2014). Floral components of Darjeeling with special reference to its forest areas. A Comprehensive District Profile of Darjeeling. S. Chaudhuri, M. Dasgupta & D.C Roy; N.L. Publishers, West Bengal.
- Dick, R.P. A review: long-term effects of agricultural systems on soil biochemical and microbial parameters. Agriculture, Ecosystems & Environment 1992; 40(1-4), 25-36.
CrossRef - Dick, R.P., Sandor, J.A., and Eash, N.S. Soil enzyme activities after 1500 years of terrace agriculture in the Colca Valley, Peru. Agriculture, Ecosystems & Environment 1994;50(2), 123-131.
CrossRef - Quilchano, C., and Marañón, T. Dehydrogenase activity in Mediterranean forest soils. Biology and Fertility of Soils 2002;35(2), 102-107.
CrossRef - Singh, S., Pandey, A., Kumar, B., and Palni, L.M.S. Enhancement in growth and quality parameters of tea [Camellia sinensis (L.) O. Kuntze] through inoculation with arbuscular mycorrhizal fungi in an acid soil. Biology and fertility of soils2010; 6(5), 427-433.
CrossRef - Miller, M., and Dick, R.P. Thermal stability and activities of soil enzymes as influenced by crop rotations. Soil Biology and Biochemistry 1995;27(9), 1161-1166.
CrossRef - Bergstrom, D.W., Monreal, C.M., Millette, J.A., and King, D.J. Spatial dependence of soil enzyme activities along a slope. Soil Science Society of America Journal 1998;62(5), 1302-1308.
CrossRef - Tilman, D., Cassman, K.G., Matson, P.A., Naylor, R., and Polasky, S. Agricultural sustainability and intensive production practices. Nature 2002;418(6898), 671-677.
CrossRef - Adesemoye, A.O., and Kloepper, J.W. Plant–microbes interactions in enhanced fertilizer use efficiency. Applied microbiology and biotechnology 2009;85(1), 1-12.
CrossRef - Łuczaj, W., and Skrzydlewska, E. Antioxidative properties of black tea. Preventive medicine 2005;40(6), 910-918.
CrossRef - Kumar, A., Kumar, A., Patel, H. Role of microbes in phosphorus availability and acquisition by plants. International journal of current microbiology and applied Sciences 2018;7(5), 1344-1347.
CrossRef - Vance, C.P., Uhde‐Stone, C., and Allan, D.L. Phosphorus acquisition and use: critical adaptations by plants for securing a nonrenewable resource. New phytologist 2003;157(3), 423-447.
CrossRef - Lambers, H., Shane, M.W., Cramer, M.D., Pearse, S.J., and Veneklaas, E.J. Root structure and functioning for efficient acquisition of phosphorus: matching morphological and physiological traits. Annals of botany 2006;98(4), 693-713.
CrossRef - Gyaneshwar, P., Kumar, G.N., Parekh, L.J., and Poole, P.S. Role of soil microorganisms in improving P nutrition of plants. Plant and soil 2002;245(1), 83-93.
CrossRef - Zoysa, A.K.N., Loganathan, P., and Hedley, M.J. Phosphorus utilisation efficiency and depletion of phosphate fractions in the rhizosphere of three tea (Camellia sinensis) clones. Nutrient Cycling in Agroecosystems 1999;53(2), 189-201.
CrossRef - Kochian, L.V., Hoekenga, O.A., and Pineros, M.A. How do crop plants tolerate acid soils? Mechanisms of aluminum tolerance and phosphorous efficiency. Annual Review of Plant Biology 2004;55, 459-493.
CrossRef - Bolan, N.S., Adriano, D.C., Naidu, R., La Mora, D., Luz, M., and Santiagio, M. (2005). Phosphorus-trace element interactions in soil-plant systems. American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America, 317-352.
CrossRef - Verma, D.P. (1993). Fertilizer management in tea. In: H.L.S. Tandon (ed.). Fertilizer Management in Commercial Crops. FDCO.
- Verma, D. P. Balanced fertilisation for sustainable productivity of tea. Fertiliser news 1997;42(4), 113-125.
- Xun, W., Jianyun, R., andBinghua, W. (1997). Potassium and magnesium for better tea production. Tea Res. Institute Hangzhou, China, and International Potash Institute Basel.