Differential growth and metal accumulation response of castor bean genotypes on a lead contaminated soil | Research Square window.SnipcartSettings = { analytics: { enabled: false } }; (function() { var accessVector = localStorage.getItem('access_vector') || ''; window.dataLayer = window.dataLayer || []; if (accessVector) { window.dataLayer.push({ user: { profile: { profileInfo: { snid: accessVector } } } }); } })(); (function(w,d,s,l,i){w[l]=w[l]||[];w[l].push({'gtm.start':new Date().getTime(),event:'gtm.js'});var f=d.getElementsByTagName(s)[0],j=d.createElement(s),dl=l!='dataLayer'?'&l='+l:'';j.async=true;j.src='https://www.googletagmanager.com/gtm.js?id='+i+dl;f.parentNode.insertBefore(j,f);})(window,document,'script','dataLayer','GTM-K279D39R'); Browse Preprints In Review Journals COVID-19 Preprints AJE Video Bytes Research Tools Research Promotion AJE Professional Editing AJE Rubriq About Preprint Platform In Review Editorial Policies Our Team Advisory Board Help Center Sign In Submit a Preprint Cite Share Download PDF Research Article Differential growth and metal accumulation response of castor bean genotypes on a lead contaminated soil Sahar Naveed, Sajid Mahmood, Wajid Ishaque This is a preprint; it has not been peer reviewed by a journal. https://doi.org/ 10.21203/rs.3.rs-3344644/v1 This work is licensed under a CC BY 4.0 License Status: Posted Version 1 posted You are reading this latest preprint version Abstract In Pakistan, probably thousands of hectares are contaminated with heavy metals. As castor plant is hyper-accumulator of heavy metals, its cultivation in the area of lead (Pb) contamination can show great potential in terms of remediation of soils. Present study aimed to evaluate the phytoremediation potential of different castor genotypes, NIAB Gold, NIAB Spineless, NIAB-2020, DS-30 and C-3 grown in pots filled with 5 kg soil, spiked with various concentrations of Pb (0, 100, 200, 400, and 800 mg kg − 1 ). Results showed that plant biomass and photosynthetic pigments reduced significantly with increasing Pb concentrations. Activities of superoxide dismutase and peroxidase were decreased significantly whereas catalase and ascorbate peroxidase were increased with increasing Pb levels in all genotypes. At 800 mg Pb kg − 1 soil, the highest catalase and ascorbate peroxidase activities of 12.23 and 64.43 mM/g FW, respectively, were recorded in DS-30 followed by NIAB-2020. The highest total soluble proteins (8.44 mg g − 1 ) were recorded in DS-30 followed by NIAB-2020 under Pb contamination at 800 mg kg − 1 soil. Lead uptake increased significantly with increasing levels of Pb and highest uptake in roots were recorded in NIAB-2020 (302 mg kg − 1 ) followed by DS-30 (299 mg kg − 1 ) under Pb contamination at 800 mg kg − 1 . All genotypes showed metal translocation factor less than 1 under all Pb levels. In conclusion, NIAB-2020 and DS-30 possessed good potential with better Pb accumulation, osmolytes production and antioxidant activities compared to other castor bean genotypes. Castor bean phytoremediation lead uptake antioxidants water relation Figures Figure 1 Introduction In the 21st century, pollution control is a major challenge due to the massive increase in pollutants produced by human activities. Among all, heavy metals and organic pollutants are known as two major factors behind soil pollution (LlnDh and LeMenkOVA, 2022). Lead is widely utilized for the manufacture of storage batteries, paints, alloy formation and casting etc (Khan et al., 2018 ). The presence of Pb in the soil is hazardous to human health due to its long-lasting residual and chance of entry in the food chain (Mühlbachová, 2011 ). Different strategies are proposed for the remediation of heavy metal contaminated soils however, phytoremediation is considered cost-effective, environmental friendly, and easy to adopt technology with good public perception (Priya et al., 2023 ). Phytoremediation, use of plants for environmental cleanup, is a promising remediation strategy. This technique is a safe and effective way to remove a variety of contaminants, with fewer negative side effects than traditional remediation strategies (Zulkernain et al., 2023 ). Castor bean, Ricinus communis L., has good potential to grow well on heavy metal contaminated soils and accumulate these metals including Pb in aerial parts. Additionally, castor possesses enormous adaptive potential in diverse habitats including resistance against drought, salinity, and climate warming, hence, suitable for marginal lands. Moreover, castor is an important non-edible industrial oil crop with various non-food and industrial applications as being used in soap, cosmetics, pharmaceutical, paints and lubricants. Therefore, phytoremediation of Pb contaminated soils using castor crop may be an environmental friendly and safe option that could give economic benefits from contaminated soils as well (Song et al., 2021 ). Various studies have reported the potential of castor bean for the phytoremediation of heavy metal contaminated soils in Brazil (Andreazza et al., 2013 ), China (Yang et al., 2017 ) and India (Boda et al., 2017 ). Heavy metal pollution is becoming an adverse problem in many cities of Pakistan including Karachi (Karim et al., 2015 ), Faisalabad (Farid et al., 2015 ), Lahore (Khan et al., 2013 ), Kasur (Afzal et al., 2014 ), Sialkot (Malik et al., 2010 ), and Peshawar (Jan et al., 2010 ). In a survey study, Afzal and coworkers ( 2014 ) determined the level of heavy metal contamination in groundwater and soil near the industrial area of Kasur. The survey results revealed that soil and groundwater in the study area are highly contaminated with all tested heavy metals specially chromium. Similarly, in case of soil, highest Pb concentration (1753 mg kg − 1 ) was detected under mining activities from Kohistan region, Gilgit Baltistan province (Muhammad et al., 2011 ). These findings indicate an alarming situation of heavy metals contamination of agricultural soils in the vicinities of industrial cities of Pakistan and demands urgent remedy for the removal of heavy metals from soils. Various lab and greenhouse studies reported the potential of different grasses (Ullah et al., 2019 ), vegetables (Akhtar et al., 2018 ) and oilseed crops (Qureshi et al., 2020 ) for the phytoremediation of heavy metal contaminated soil. However, no mechanism based study is available regarding phytoremediation of Pb-contaminated soils using castor bean. Therefore, present study was designed to evaluate the growth, physiology and Pb uptake efficacy of castor genotypes for phytoremediation of Pb contaminated soils. Materials and methods Experimental structure and treatment plan A pot experiment was conducted to evaluate the growth, physiological and phytoremediation response of different castor genotypes on Pb contaminated soil under wire house conditions at the Nuclear Institute for Agriculture and Biology (NIAB) Faisalabad, Pakistan with coordinates 31.4504 N and 73.1350 E. Seeds of five castor genotypes (NIAB Gold, NIAB Spineless, NIAB-2020, DS-30 and C-3) were collected from Plant Breeding and Genetics Division (PBGD), NIAB. Plastic pots (20 × 22.5 cm) were filled with thoroughly mixed, air-dried and precisely sieved soil (5 kg) using 2 mm mesh. The well prepared soil was spiked with different concentrations of Pb (0, 100, 200, 400, and 800 mg kg − 1 soil) prior to 3 months of sowing to equilibrate the metal in the soil. For this, above stated Pb concentrations were firstly calculated and then applied in solution form using lead nitrate of Sigma Aldrich (purity ≥ 99.0%). Soil without any treatment of Pb was considered as control. After the accomplishment of the required time period, pre-soaked seeds were sown in each pot with three replications following completely randomized design (CRD) with factorial settings. Plants were grown under natural environment with average temperatures of 30–35°C (night-day). The basal dose of fertilizer (NPK) was calculated and applied to each pot. Addition of nitrogen in soil through lead nitrate was adjusted while calculating the fertilizer dose (Ahmad, 2010 ). Physicochemical analysis of the experimental soil Soil was collected in bulk from the experimental site of NIAB and categorized for different physicochemical analysis (Table 1 ). Bouyoucos hydrometer protocol was followed for the determination of soil texture (Lotfy and Mostafa, 2014 ). Saturated paste was prepared to determine the pH of the soil using pH meter (ST-5000-OHAUS-USA) whereas soil extract was used to determine EC using EC meter (a-AB33EC, OHAUS, USA). Total nitrogen and available phosphorous were analyzed following Kjeldahl (Bremner, 1960 ) and Olsen ( 1954 ) method, respectively. Organic matter was determined as described by Walkley and Black ( 1934 ). Total Pb in soil was determined by the method as described by Ullah et al. ( 2020 ). Table 1 Physiochemical analysis of the experimental soil Sand (%) Silt (%) Clay (%) Texture pH EC (dS m − 1 ) Total N (%) Available P (mg kg − 1 ) O.M (%) Total Pb (mg kg − 1 ) 58 34.7 4.5 Sandy loam 7.65 2.05 0.081 5.9 0.99 N.D O.M = Organic matter, N.D = Not detected Gas exchange parameters Stomatal conductance, transpiration and photosynthetic rate of the plants were measured through Decagon ( 2011 ) method in the morning hours using a porometer (Lincor.Inc steady state porometer). Estimation of relative water content and electrolyte leakage Relative water content (RWC) of the castor bean genotypes were determined using the method as described by Teulat et al. ( 2003 ) whereas electrolyte leakage of castor genotypes were determined by the method as described by Yang et al. ( 1996 ). Plant growth parameters Plants were harvested after 2 months and data regarding plant height and shoot fresh weight were recorded. Roots were washed thoroughly with tap water using plastic mesh to remove the soil particles and then with deionized water to determine root fresh weight. Shoot and root samples were oven dried at 70 ° C for 72 hours to record dry weight. Determination of photosynthetic activity Arnon ( 1949 ) protocol was opted to determine photosynthetic pigments in fresh leaves of castor genotypes. Determination of antioxidants enzymes After five weeks of germination, fresh samples (0.2 g) of castor leaves were ground and homogenized in 0.05 M phosphate buffer solution (pH 7.8). The homogenized mixture was filtered and centrifuged at 12,000 rpm for 10 minutes at 4 ° C. Superoxide dismutase activity was measured by following Giannopolitis and Ries ( 1977 ) protocol at 560 nm. Pütter ( 1974 ) procedure was opted to determine peroxidase activity. The increase in absorbance due to the oxidation of guaiacol was measured spectrophotometrically at 470 nm. Catalase activity was determined by monitoring the reduction in the absorbance at 240 nm using the procedure as described by Aebi ( 1984 ). Ascorbate peroxidase (APX) activity was determined by the method as described by Nakano and Asada ( 1981 ). Determination of total soluble proteins, total soluble sugars and total phenolic contents Total soluble protein (TSP) was determined as described by Bradford ( 1976 ). Total soluble sugars (TSS) were analyzed spectrophotometrically according to Riazi et al. ( 1985 ) procedure. Micro-colorimetric method was followed for the determination of total phenolic contents (TPC) (Ainsworth and Gillespie, 2007 ). Lead concentration in shoot and root The heavy metal analysis was performed following the protocol of Ullah et al. ( 2020 ) with some modifications. Ground and oven-dried shoot and root samples were digested with nitric acid and perchloric acid (8:2 v/v) on a hot plate until the sample become colorless. After cooling, the digested samples were diluted to 50 mL with distilled water and filtered through Whatman No. 42 filter paper. The metal analysis was carried out using atomic absorption spectroscopy (Analytikjena, contrAA 800D, Germany). Statistical analysis The data obtained were analyzed using two-way analysis of variance (ANOVA) (Steel et al., 1997 ) and the means were compared by applying the least significance difference test at p ≤ 0.05. Data represent the mean of three replicates. The statistical analysis was conducted using the statistical software Statistix 8.1. Mean data of all parameters in the study were subjected to perform Principal Component Analysis (PCA) using XL-STAT software version 2014. Results and Discussion Effect of Pb contamination on plant growth attributes The analysis of variance showed a significant influence of Pb treatments on the growth attributes of different castor bean genotypes. Plant height was significantly decreased ( p ≤ 0.05) with the increasing concentrations of Pb in the soil. At 800 mg Pb kg − 1 soil, NIAB-2020 showed better performance against Pb with an average height of 29.3 cm followed by DS-30 (28.0 cm) as compared to other genotypes. Shoot fresh biomass, root dry weight and shoot dry biomass were decreased due the presence of Pb. At 800 mg Pb kg − 1 soil, the highest shoot fresh biomass up to 9.23 g plant − 1 was observed in DS-30 followed by NIAB-2020 and C-3 i.e. 8.15 and 7.39 g plant − 1 whereas maximum shoot dry weight and root dry weight i.e. 1.31 and 0.26 g plant − 1 were recorded in NIAB-2020, respectively followed by DS-30 (Table 2 ). Table 2 Effect of different levels of lead contamination of soil on the agronomic parameters of different castor genotypes Pb (mg kg − 1 ) soil Genotypes HT (cm) FBM (g plant − 1 ) DBM (g plant − 1 ) RDW (g plant − 1 ) 0 NIAB-G 39.33 c 27.77 b 2.23 c 0.50 d NIAB-SPN 39.66 c 31.11 a 2.44 b 0.57 c NIAB- 2020 46.66 b 32.31 a 2.69 a 0.69 a DS-30 52.33 a 32.34 a 2.67 a 0.66 b C-3 45.66 b 27.93 b 2.47 b 0.57 c 100 NIAB-G 38.00 cde 24.92 cd 1.93 e 0.42 f NIAB-SPN 38.33 cd 24.95 cd 2.09 d 0.48 e NIAB- 2020 39.33 c 27.19 bc 2.21 cd 0.49 e DS-30 38.66 cd 26.92 bc 2.19 cd 0.49 e C-3 38.33 cd 26.06 bc 2.14 cd 0.43 f 200 NIAB-G 31.66 fg 21.20 ef 1.78 f 0.37 j NIAB-SPN 33.33 f 21.60 e 1.53 g 0.39 i NIAB- 2020 37.00 de 22.66 de 1.92 e 0.41 g DS-30 36.00 e 22.31 e 1.93 e 0.41 gh C-3 33.66 f 21.30 e 1.52 g 0.40 hi 400 NIAB-G 30.00 ghi 15.93 g 1.31 hij 0.30 m NIAB-SPN 31.00 gh 16.04 g 1.35 hi 0.32 l NIAB- 2020 31.00 gh 20.58 ef 1.50 g 0.33 l DS-30 31.00 gh 20.94 ef 1.51 g 0.35 k C-3 30.33 gh 18.37 f 1.43 gh 0.32 l 800 NIAB-G 23.66 k 6.31 i 1.09 k 0.13 p NIAB-SPN 22.00 k 6.52 i 1.19 jk 0.19 o NIAB- 2020 29.33 hi 8.15 hi 1.31 hij 0.26 n DS-30 28.00 ij 9.23 h 1.29 ij 0.20 o C-3 26.00 j 7.39 hi 1.25 ij 0.19 o LSD 2.25 2.44 0.12 0.02 Data represent the mean of three replicates. Means within the same column having different letters are significantly different at p ≤ 0.05 according to LSD. (Pb = lead); (NIAB-G = NIAB GOLD, NIAB-SPN = NIAB SPINELESS) and (Ht = Plant Height, FBM = Shoot fresh Biomass, DBM = Dry Biomass, RDW = Root dry weight). Effect of Pb contamination of soil on physiological parameters Table 3 illustrates the effect of Pb on the physiological parameters of different castor genotypes. The RWC of all genotypes were slightly affected with the increasing concentrations of Pb ( p ≤ 0.05). Comparing the varieties against each level of Pb, RWC showed a faint decreasing trend from 0 to 200 mg kg − 1 . At 800 mg Pb kg − 1 soil, NIAB-2020 showed maximum retention of water in leaves (90%) followed by DS-30 (82%), NIAB Gold (80%), NIAB spineless (78%) and C-3 (70%) due to the production of osmolytes. Electrolyte leakage is the key response of plant against any abiotic stress. Electrolyte leakage was increased significantly with the increasing concentration of Pb in the soil ( p ≤ 0.05). At 800 mg Pb kg − 1 soil, maximum electrolyte leakage was observed in NIAB spineless and NIAB Gold as compared to other genotypes. Table 3 Effect of different levels of lead contamination of soil on the physiological parameters of different castor genotypes Pb (mg kg − 1 ) soil Genotypes RWC (%) EL (%) SC (mmol m − 2 s − 1 ) TR (mmol m − 2 s − 1 ) PR (umol m − 2 s − 1 ) 0 NIAB-G 99.00 a-d 9.16 qr 11.36 c 2.55 ab 383.53 cd NIAB-SPN 99.40 abc 8.42 rs 12.40 b 2.52 abc 427.16 bc NIAB- 2020 100.00 a 6.67 s 12.87 b 2.63 a 454.50 ab DS-30 100.00 a 7.23 s 15.76 a 2.58 ab 485.89 a C-3 99.80 ab 10.81 pq 12.20 b 2.52 abc 346.52 de 100 NIAB-G 95.62 a-f 12.80 mno 10.64 cd 2.44 b-e 287.41 fgh NIAB-SPN 96.02 a-f 13.85 lmn 10.91 cd 2.45 b-e 304.20 efg NIAB- 2020 98.80 a-d 11.49 op 11.26 c 2.50 abc 332.52 e DS-30 97.93 a-e 12.47 nop 11.26 c 2.49 a-d 325.09 ef C-3 96.90 a-f 14.49 klm 10.99 cd 2.46 a-e 314.71 ef 200 NIAB-G 93.37 a-f 15.36 kl 9.38 fg 2.31 efg 242.76 hi NIAB-SPN 93.82 a-f 16.19 jk 9.39 fg 2.32 d-g 245.29 hi NIAB- 2020 94.25 a-f 14.75 kl 10.38 de 2.42 b-e 251.62 hi DS-30 95.01 a-f 14.49 klm 9.78 ef 2.42 b-e 268.39 ghi C-3 93.82 a-f 17.19 ij 9.62 efg 2.37 c-f 230.30 ij 400 NIAB-G 91.04 f 37.68 f 7.00 jk 2.06 hij 193.41 jkl NIAB-SPN 91.87 ef 24.54 g 7.68 ij 2.11 hi 183.64 klm NIAB- 2020 93.06 b-f 17.36 ij 8.85 gh 2.14 ghi 223.93 ijk DS-30 92.82 c-f 18.25 i 8.09 hi 2.20 fgh 194.73 jkl C-3 92.58 def 20.24 h 7.92 i 2.05 h-k 177.87 lm 800 NIAB-G 80.40 g 109.92 b 5.51 m 1.92 jkl 140.63 mn NIAB-SPN 78.69 g 223.59 a 6.09 lm 1.88 kl 157.45 lmn NIAB- 2020 90.79 f 81.85 e 6.65 kl 2.00 ijk 165.68 lm DS-30 82.26 g 102.36 d 6.80 kl 1.97 i-l 173.37 lm C-3 70.59 h 106.26 c 5.44 m 1.81 l 119.66 n LSD 6.76 1.81 0.81 0.18 44.91 Data represent the mean of three replicates. Means within the same column having different letters are significantly different at p ≤ 0.05 according to LSD. (Pb = lead); (NIAB-G = NIAB GOLD, NIAB-SPN = NIAB SPINELESS) and (RWC = Relative Water content, EL = Electrolyte Leakage, SC = Stomatal Conductance, TR = Transpiration rate, PR = Photosynthesis rate). Observing the gas exchange parameters, stomatal conductance, transpiration and photosynthetic rate were significantly reduced with the increasing concentrations of Pb ( p ≤ 0.05). A gradual decrease in stomatal conductance due to 100 to 800 mg kg − 1 Pb in soil disturbed the transpiration rate and photosynthesis in castor genotypes. At 800 mg kg − 1 , significant reduction in photosynthetic activity was observed in C-3 and NIAB Gold i.e. 119.6 and 140.63 mmol m − 2 s − 1 respectively, while highest photosynthetic activity was recorded in DS-30 and NIAB-2020. Effects of Pb on leaf pigment contents The effect of Pb on the pigment content of the castor genotypes resulted in significant decreasing trend ( p ≤ 0.05) with increasing metal stress. Interestingly, NIAB-2020 exhibited highest total chlorophyll and carotenoid content up to 8.61 and 3.59 mg g − 1 respectively, as compared to other genotypes at 800 mg kg − 1 (Table 4 ). Table 4 Effect of different levels of lead contamination of soil on the photosynthetic pigments of different castor genotypes Pb (mg kg − 1 ) soil Genotypes Chl a mg g − 1 Chl b mg g − 1 Total Chl mg g − 1 Carotenoids mg g − 1 0 NIAB-G 5.42 ab 4.65 ab 10.0 abc 4.15 b NIAB-SPN 5.40 ab 4.64 ab 10.0 abc 4.15 b NIAB- 2020 5.47 a 4.72 a 10.1 a 4.20 a DS-30 5.47 a 4.65 ab 10.1 ab 4.16 ab C-3 5.40 ab 4.63 ab 10.0 abc 4.14 b 100 NIAB-G 5.13 def 4.58 b 9.72 d 4.04 c NIAB-SPN 5.13 def 4.59 ab 9.71 d 4.04 c NIAB- 2020 5.23 bcd 4.62 ab 9.85 cd 4.05 c DS-30 5.35 abc 4.59 ab 9.94 bc 4.05 c C-3 5.19 cde 4.27 c 9.46 e 4.04 c 200 NIAB-G 4.98 f-j 4.24 c 9.23 fgh 4.01 c NIAB-SPN 5.02 e-i 4.23 c 9.24 fgh 4.02 c NIAB- 2020 5.11 d-g 4.26 c 9.37 ef 4.04 c DS-30 5.07 d-h 4.25 c 9.32 efg 4.03 c C-3 4.97 f-k 4.23 c 9.20 fgh 3.96 d 400 NIAB-G 4.89 h-l 4.16 c 9.05 h 3.71 f NIAB-SPN 4.86 i-l 3.88 d 8.74 i 3.90 e NIAB- 2020 4.92 g-k 4.19 c 9.11 gh 3.95 de DS-30 4.97 f-k 4.21 c 9.18 fgh 3.92 de C-3 4.87 i-l 3.82 de 8.69 ij 3.68 f 800 NIAB-G 4.66 m-p 3.76 def 8.42 klm 3.50 h NIAB-SPN 4.72 l-o 3.76 def 8.47 jkl 3.58 g NIAB- 2020 4.84 i-m 3.77 def 8.61 ijk 3.59 g DS-30 4.82 j-m 3.76 def 8.58 ijk 3.59 g C-3 4.78 k-n 3.75 def 8.54 i-l 3.58 g LSD 0.19 0.13 0.21 0.05 Data represent the mean of three replicates. Means within the same column having different letters are significantly different at p ≤ 0.05 according to LSD. (Pb = lead); (NIAB-G = NIAB GOLD, NIAB-SPN = NIAB SPINELESS) and (Chl a = Chlorophyll a, Chl b = Chlorophyll b, Total Chl = Total Chlorophyll). Effect of Pb on the biochemical profile of castor bean Results revealed that in all genotypes, SOD and POD showed negative correlation whereas an increasing trend of CAT and APX were recorded with increasing concentrations of Pb ( p ≤ 0.05) as shown in Table 5 . Interestingly, at 800 mg kg − 1 , highest CAT and APX activities were recorded in DS-30 (12.23 and 64.43 mM/g FW) followed by NIAB-2020 (12.13 and 64.31 mM/g FW), respectively (Table 5 ). Table 5 Effect of different levels of lead contamination of soil on the enzymatic antioxidants of different castor genotypes Pb (mg kg − 1 ) soil Genotypes SOD (U/g FW) POD (mM/g FW) CAT (mM/g FW) APX (mM/g FW) 0 NIAB-G 2196.7 cde 8.19 bc 3.86 i 30.73 NIAB-SPN 2300.7 c 8.29 bc 1.86 j 31.53 j NIAB- 2020 3284.0 a 12.07 a 4.63 hi 38.10 i DS-30 2979.5 b 11.75 a 4.70 hi 38.50 i C-3 2251.1 cd 8.39 b 4.20 i 29.29 k 100 NIAB-G 1993.3 ef 6.41 ef 5.10 ghi 40.77 h NIAB-SPN 2045.8 de 5.97 fg 5.60 gh 40.53 h NIAB- 2020 2142.2 cde 7.32 d 5.70 gh 53.37 f DS-30 2078.3 cde 7.46 cd 5.83 fgh 53.40 f C-3 2032.5 de 7.01 de 5.10 ghi 42.26 g 200 NIAB-G 1583.8 g-j 5.39 ghi 7.03 ef 57.24 e NIAB-SPN 1780.4 fgh 5.66 fgh 8.20 de 59.12 d NIAB- 2020 1801.4 fg 5.82 fg 8.40 d 59.38 cd DS-30 1794.7 fg 5.78 fg 8.30 de 59.13 cd C-3 1663.0 ghi 5.30 g-j 6.30 fg 53.58 f 400 NIAB-G 1454.9 i-l 4.51 jk 8.80 cd 59.75 bcd NIAB-SPN 1548.4 ijk 4.58 ijk 8.40 d 59.64 bcd NIAB- 2020 1568.5 h-k 5.27 g-j 9.20 bcd 60.73 b DS-30 1582.8 g-j 5.14 g-j 9.30 bcd 60.70 b C-3 1520.8 ijk 4.90 hij 9.13 bcd 60.26 bc 800 NIAB-G 1059.6 n 3.03 m 9.80 bc 63.45 a NIAB-SPN 1278.3 lmn 2.17 n 9.96 bc 64.02 a NIAB- 2020 1388.1 j-m 3.92 kl 12.13 a 64.31 a DS-30 1357.5 klm 3.56 lm 12.23 a 64.43 a C-3 1182.8 mn 3.24 lm 10.33 b 63.45 a LSD 224.4 0.83 1.29 1.13 Data represent the mean of three replicates. Means within the same column having different letters are significantly different at p ≤ 0.05 according to LSD. (Pb = lead); (NIAB-G = NIAB GOLD, NIAB-SPN = NIAB SPINELESS) and (SOD = Superoxide dismutase, POD = Peroxidase, CAT = Catalase, APX = Ascorbate Peroxidase). A vigorous increase in TSS and TPC from 200 to 800 mg kg − 1 were observed in all castor genotypes. At 800 mg kg − 1 , NIAB-2020, DS-30 and NIAB Spineless showed an equal production of soluble sugars of 18.6 mg g − 1 . With reference to phenolic contents, NIAB-2020 produced two times more phenolic contents up to 0.49 mg g − 1 as compared to other genotypes. Total soluble proteins showed negative relation to Pb concentrations. At 800 mg kg − 1 , DS-30 produced 8.44 mg g − 1 total soluble proteins followed by NIAB-2020, NIAB spineless, NIAB Gold and C-3 (Table 6 ). Table 6 Effect of different levels of lead contamination on the non-enzymatic antioxidants of different castor genotypes Pb (mg kg − 1 ) Genotypes TSP (mg/g) TSS (mg/g) TPC (mg/g) 0 NIAB-G 11.33 b 13.99 e 0.14 k NIAB-SPN 11.60 ab 13.99 e 0.14 k NIAB- 2020 11.90 ab 14.01 e 0.15 k DS-30 12.10 a 14.09 de 0.15 k C-3 11.60 ab 14.01 e 0.14 k 100 NIAB-G 10.00 c 14.09 de 0.15 k NIAB-SPN 10.03 c 14.12 de 0.19 j NIAB- 2020 11.23 b 14.20 d 0.21 hi DS-30 11.25 b 14.20 d 0.20 ij C-3 11.23 b 14.12 de 0.19 j 200 NIAB-G 9.02 efg 18.42 c 0.21 ghi NIAB-SPN 9.04 efg 18.42 c 0.22 gh NIAB- 2020 9.94 cd 18.44 bc 0.23 g DS-30 9.66 cde 18.44 bc 0.23 g C-3 9.26 def 18.42 c 0.21 ghi 400 NIAB-G 8.48 ghi 18.44 bc 0.28 f NIAB-SPN 8.71 fgh 18.54 abc 0.30 ef NIAB- 2020 8.90 fgh 18.54 abc 0.31 de DS-30 9.01 efg 18.59 ab 0.31 de C-3 8.90 fgh 18.54 abc 0.31 de 800 NIAB-G 7.59 j 18.59 ab 0.32 d NIAB-SPN 7.83 ij 18.69 a 0.34 c NIAB- 2020 8.21 hij 18.69 a 0.49 a DS-30 8.44 ghi 18.69 a 0.38 b C-3 6.77 k 18.59 ab 0.34 c LSD 0.68 0.15 0.02 Data represent the mean of three replicates. Means within the same column having different letters are significantly different at p ≤ 0.05 according to LSD. (Pb = lead); (NIAB-G = NIAB GOLD, NIAB-SPN = NIAB SPINELESS) and (TSS = Total Soluble sugars, TSP = Total Soluble Proteins, TPC = Total Phenolic contents). Lead uptake in castor genotypes Results have shown a significant increase in the concentration of Pb in plant tissues of all castor genotypes ( p ≤ 0.05). Elemental analysis have shown higher concentration of Pb in roots as compared to shoots. At 800 mg kg − 1 , highest concentration of Pb in the roots were recorded in NIAB-2020 (302.0 mg kg − 1 ) followed by DS-30 (299.3 mg kg − 1 ). The highest translocation factor of 0.99 was observed in NIAB-2020. The bioconcentration factor of roots (BCFroot) increased with the increasing concentration of Pb as compared to bioconcentration factor of shoots (BCFshoot). At 800 mg kg − 1 , NIAB-2020 showed the maximum value of 3.59 followed by DS-30 (3.29) (Table 7 ). Table 7 Determination of different levels of lead in the shoot and root of different castor genotypes Pb (mg kg − 1 ) Genotypes Shoot (mg kg − 1 ) Root (mg kg − 1 ) TF BCFshoots BCFroots 0 NIAB-G N/D N/D N/D N/D N/D NIAB-SPN N/D N/D N/D N/D N/D NIAB- 2020 N/D N/D N/D N/D N/D DS-30 N/D N/D N/D N/D N/D C-3 N/D N/D N/D N/D N/D 100 NIAB-G 28.67 o 43.67 o 0.63 m 0.93 o 1.38 l NIAB-SPN 29.83 o 50.33 n 0.64 lm 0.94 o 1.71 k NIAB- 2020 33.67 n 51.50 n 0.65 klm 1.20 mn 1.81 k DS-30 37.00 m 50.50 n 0.66 kl 1.30 m 1.80 k C-3 32.00 n 43.67 o 0.64 klm 1.09 n 1.41 l 200 NIAB-G 81.00 j 90.33 m 0.68 i 1.86 k 2.45 j NIAB-SPN 78.33 k 99.67 kl 0.68 ij 1.75 kl 2.64 hi NIAB- 2020 83.67 i 103.00 j 0.71 gh 2.07 ij 2.70 gh DS-30 82.00 ij 100.67 k 0.69 hi 2.05 j 2.66 h C-3 71.00 l 98.00 l 0.66 jk 1.70 l 2.52 ij 400 NIAB-G 122.67 h 190.00 hi 0.72 g 2.12 ij 2.87 ef NIAB-SPN 123.00 h 189.00 i 0.78 f 2.18 hi 2.82 fg NIAB- 2020 135.00 f 196.00 g 0.81 e 2.39 fg 2.92 ef DS-30 139.00 e 199.00 f 0.86 d 2.50 ef 2.96 de C-3 125.67 g 191.67 h 0.81e 2.29 gh 2.88 ef 800 NIAB-G 252.00 d 288.00 e 0.86 d 2.58 de 2.98 de NIAB-SPN 253.00 d 290.00 d 0.89 c 2.68 cd 3.05 cd NIAB- 2020 299.23 a 302.00 a 0.99 a 2.92 a 3.59 a DS-30 289.17 b 299.33 b 0.96 b 2.89 ab 3.29 b C-3 272.80 c 293.00 c 0.94 b 2.78 bc 3.16 c LSD 2.06 1.71 0.02 0.12 0.12 Data represent the mean of three replicates. Means within the same column having different letters are significantly different at p ≤ 0.05 according to LSD. (Pb = lead); (NIAB-G = NIAB GOLD, NIAB-SPN = NIAB SPINELESS) and (N/D = Not Detected, TF = Translocation factor, BCF = Bio concentration factor). Principal component analysis Principal component analysis was performed to analyze the visual comparison of castor genotypes, and to collect information about the inter-relationship between variables at different levels of Pb as shown in Fig. 1. Morpho-physiological parameters, pigment content, antioxidant activities, osmolytes, and Pb uptake were investigated using PCA. Biplot showed that among 8 principal components, 4 have Eigenvalues > 1, while remaining components have not been discussed due to Eigenvalues < 1. At 0 mg kg − 1 , EL showed strong association with NIAB Gold, NIAB Spineless and C-3 whereas RWW, TF, TSS, CAT, DBM, RWC, FBM, Pb in root and shoot, chlorophyll a, total chlorophyll and bioconcentration factor in roots were linked to DS-30. Ascorbate peroxidase, SC, PR, SOD, TPC, and chlorophyll b co-occurred with NIAB-2020 (Fig. 1-a). It have been observed that with the increase in Pb contamination in soil, major agronomic, physiological and biochemical parameters were strongly connected to DS-30 and NIAB-2020 as compared to NIAB Gold, NIAB Spineless and C-3. At 100 and 200 mg kg − 1 , CAT, TPC, RWC, TSS, APX, TSP, SOD and POD along with other parameters aids in the survival of DS-30 and NIAB-2020 under Pb stress (Fig. 1-b, c). Similar responses were observed at 400 and 800 mg kg − 1 in DS-30 and NIAB-2020 (Fig. 1-d, e). Lead exposure have a variety of negative effects on plant growth including physiological disruptions, decreased biomass production, membrane and structural damage and reduced pigment contents. The extent of these effects depends on the type of plant and the concentration of Pb in soil. Our present study have shown that plant height, shoot fresh weight, shoot dry weight and root dry weight in all castor genotypes were decreased due to Pb contamination in soil. Physiological parameters including RWC, EL, SC, TR and PR were also decreased. Photosynthetic pigments including chlorophyll a, b and carotenoids were reduced due to Pb stress. Plant height was decreased with the increasing concentrations of Pb. Similar trend was reported in Brachiaria mutica (Ullah et al., 2021 ). This suggests that lead interfered more strongly with the plant's metabolic processes over time. It has been observed that shoot fresh and dry biomass declined in Parthenium hysterophorus (Javaid et al., 2023 ) due to Pb contamination. Comparable outcomes in terms of shoot fresh and dry biomass in the present study under higher level of Pb contamination were recorded in castor bean. Likewise, a declining trend was observed in root dry weight with increasing levels of Pb contamination. Similar effects of Pb contamination on root dry weight have also been reported in Solanum lycopersicum (Ma et al., 2022 ) and Sesamum indicum (Naveed et al., 2023 ). Relative water content (RWC) is an important parameter in water relation studies. Upon exposure to Pb stress, relative water content was decreased with the increasing Pb concentrations. Previous studies on Helianthus annuus also showed the similar results (Al-Jobori and Kadhim, 2019 ). In castor bean, electrolyte leakage was increased with the increasing Pb concentrations in soil. Our findings are consistent with the previous studies which reported that exposure to Ni and Pb can increase electrolyte leakage in Coronopus didymus (Sidhu et al., 2016 ). Observing the gas exchange attributes, stomatal conductance, transpiration and photosynthetic rate were declined with the increasing concentrations of Pb in soil as reported in Corchorus capsularis (Saleem et al., 2020 ). Exposure to lead (Pb) can have a significant impact on the amount and type of pigments synthesis in plants. Different studies on tomato (Ma et al., 2022 ) supported the results recorded in castor bean under Pb contamination. The concentrations of chlorophyll and carotenoids were reduced as Pb disrupted the structure and function of enzymes involved in chlorophyll synthesis and directly interact with the components of photosystem II (PSII). Superoxide dismutase is especially important in providing first-line resistance to the toxic impact of ROS (Zhou et al., 2022 ). In general, antioxidant activity is promoted under lower levels of heavy metal stress, but it decreases at higher levels of stress. In this study, SOD and POD was decreased with the increasing concentrations of Pb. The decline in SOD and POD in our study may be assigned to Pb stress that damaged the antioxidant enzymatic systems. Similarly, decreasing trend of SOD and POD has been observed in Brachiaria mutica . Conversely, CAT and APX were increased upon exposure to Pb stress. For example, in E. argyi , a concentration-dependent increase in CAT activity was observed in response to Pb toxicity. This suggests that CAT activity may be one of the mechanisms by which castor bean plants detoxify Pb. The increase in CAT activity can be explained by an increase in its substrate (H 2 O 2 ) and could be an adaptive mechanism of the plant to balance H 2 O 2 level (Khan et al., 2018 ). The production of total soluble proteins in castor bean has been decreased under Pb stress. Previously, under Pb stress Brassica rapa have shown a decline in concentration of TSP (Ahmad et al., 2023). Results showed that TPC have been increased under Pb stress. Similar increase in phenol content has been reported in winter wheat plants under Pb contamination (Jańczak-Pieniążek et al., 2022 ). Studies have shown that the concentration of soluble sugars in plants increased markebly when exposed to stress. This is a possible mechanism that plants use to mitigate the negative effects of Pb stress. Our findings have shown an abrupt increase in the concentration of total soluble sugars from 200–800 mg kg − 1 . In a previous study, Phaseolus vulgaris showed significant increase in reducing sugars under Pb contamination (Aldoobie et al., 2013). Castor bean has been well known for its hyperaccumulating efficiency to uptake various heavy metals from soil. Results have shown that accumulation of Pb was higher in roots of castor as compared to shoots. The plant's extensive root system aids in binding and immobilizing lead ions, thereby reducing their movement in the soil profile (Wani et al., 2023 ). The accumulation of lead is known to increase in a concentration-dependent manner, but its translocation from root to shoot is low in plants such as Zea mays (Yang et al., 2016 ), Cannabis sativa (Ćaćić et al., 2019 ), Helianthus annuus (Ullah et al., 2011 ), Brachiaria mutica (Khan et al., 2018 ), and Sesbania grandiflora (Malar et al., 2014 ). Hence, phytoremediation using castor bean could be a promising technology for the removal of heavy metals from contaminated soil. This can help to certify the security of agricultural products, such as fruits and vegetables which are an important part of the human food. Conclusion The current study has revealed that Pb toxicity negatively affects the agronomic and physiological parameters, pigment content as well as some osmolytes in castor genotypes due to ROS production and reduced antioxidant capacities. Hyper-Accumulation of Pb was higher in castor roots as compared to shoots. NIAB-2020 and DS-30 showed the better performance as compared to NIAB Gold, NIAB Spineless and C-3. Thus, castor bean has demonstrated its efficiency in multiple phytoremediation mechanisms, making it a versatile tool for remediating lead-contaminated soils. Declarations Acknowledgments Authors are extremely obliged to NIAB-C, PIEAS, for providing the permission and analytical facilities to carry out the PhD study and complete the research. Ethics approval and consent to participate All authors have read, understood, and have complied as applicable with the statement on "Ethical responsibilities of Authors" as found in the Instructions for Authors and are aware that with minor exceptions, no changes can be made to authorship once the paper is submitted. Moreover, all authors consent to participate. Availability of data and material The authors confirm that the data supporting the findings of this study are available within the article. Competing interests Authors declare no competing interest. Funding This research did not receive any specific grant from funding agencies in the public, commercial, or Not for profit sectors Authors contributions Sahar Naveed: literature review, conceptualization, methodology, modeling, result analysis, conclusion, and writing the original manuscript. Sajid Mahmood: conceptualization, supervision/guidance, and reviewed original manuscript. Wajid Ishaque: technical support and helped in concluding the manuscript. References Aebi, H.,1984. Catalase in vitro. Methods Enzymol.105, 121–126. doi: 10.1016/S0076 6879(84) 0 5016-3. Afzal, M., Shabir, G., Iqbal, S., Mustafa, T., Khan, Q. M., & Khalid, Z. M. (2014). Assessment of heavy metal contamination in soil and groundwater at leather industrial area of Kasur, Pakistan. CLEAN–Soil, Air, Water , 42(8), 1133-1139. doi: 10.1002/clen.201100715. Ahmad, F. (2010). Leptochloa fusca cultivation for utilization of salt-affected soil and water resources in Cholistan Desert. Sociedade & Natureza , 22, 141-149. doi.org/10.1590/S1982-45132010000100010. Ahmed, S., Khan, M., & Sardar, R. (2023). Glutathione primed seed improved lead-stress tolerance in Brassica rapa L. through modulation of physio-biochemical attributes and nutrient uptake. International Journal of Phytoremediation , 1-11. doi: 10.1080/15226514.2023.2178380. Ainsworth, E. A., & Gillespie, K. M. (2007). Estimation of total phenolic content and other oxidation substrates in plant tissues using Folin–Ciocalteu reagent. Nature protocols , 2(4), 875-877. doi: 10.1038/nprot.2007.102. Akhtar, M. J., Ullah, S., Ahmad, I., Rauf, A., Nadeem, S. M., Khan, M. Y., & Bulgariu, L. (2018). Nickel phytoextraction through bacterial inoculation in Raphanus sativus . Chemosphere , 190, 234-242. doi:10.1016/j.chemosphere.2017.09.136. Aldoobie, N. F., & Beltagi, M. S. (2013). Physiological, biochemical and molecular responses of common bean ( Phaseolus vulgaris L.) plants to heavy metals stress. African Journal of Biotechnology , 12(29), pp. 4614-4622. doi: 10.5897/AJB2013.12387. Al-Jobori, K. M., & Kadhim, A. K. (2019). Evaluation of sunflower ( Helianthus annuus L.) for phytoremediation of lead contaminated soil. Journal of Pharmaceutical Sciences and Research , 11(3), 847-854. doi: 10.5539/ep.v3n2p65. Andreazza, R., Bortolon, L., Pieniz, S., & Camargo, F. A. O. (2013). Use of high-yielding bioenergy plant castor bean ( Ricinus communis L.) as a potential phytoremediator for copper-contaminated soils. Pedosphere , 23(5), 651-661. doi: 10.1016/S1002-0160(13)60057-0. Arnon, D. I. (1949). Copper enzymes in isolated chloroplasts. Polyphenoloxidase in Beta vulgaris. Plant physiology , 24(1), 1. doi: 10.1104/pp.24.1.1. Boda, R. K., Majeti, N. V. P., & Suthari, S. (2017). Ricinus communis L.(castor bean) as a potential candidate for revegetating industrial waste contaminated sites in peri-urban Greater Hyderabad: remarks on seed oil. Environmental Science and Pollution Research , 24, 19955-19964. doi: 10.1007/s11356-017-9654-5. Bradford, M. M. (1976). A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. Analytical biochemistry , 72(1-2), 248-254. doi: 10.1016/0003-2697(76)90527-3. Bremner, J. (1960). Determination of nitrogen in soil by the Kjeldahl method. The Journal of Agricultural Science , 55(1), 11-33. doi:10.1017/S0021859600021572. Ćaćić, M., Perčin, A., Zgorelec, Ž., & Kisić, I. (2019). Evaluation of heavy metals accumulation potential of hemp ( Cannabis sativa L.). Journal of Central European Agriculture , 20(2), 700-711. Decagon (2011). Leaf Porometer Upgraded Model Sc-1. Pullman, WA: Decagon Devices, Inc. Farid, G., Sarwar, N., Saifullah, A. A., Ghafoor, A., & Rehman, M. (2015). Heavy metals (Cd, Ni and Pb) contamination of soils, plants and waters in Madina town of Faisalabad metropolitan and preparation of GIS based maps. Advances in Crop Science and Technology , 4(2), 693-706. doi: 10.4172/2329-8863.1000199. Giannopolitis, C. N., & Ries, S. K. (1977). Superoxide dismutases: I. Occurrence in higher plants. Plant physiology , 59(2), 309-314. doi: 10.1104/pp.59.2.309. Jan, F. A., Ishaq, M., Ihsanullah, I., & Asim, S. M. (2010). Multivariate statistical analysis of heavy metals pollution in industrial area and its comparison with relatively less polluted area: a case study from the City of Peshawar and district Dir Lower. Journal of hazardous materials , 176(1-3), 609-616. doi: 10.1016/j.jhazmat.2009.11.073. Jańczak-Pieniążek, M., Cichoński, J., Michalik, P., & Chrzanowski, G. (2022). Effect of heavy metal stress on phenolic compounds accumulation in winter wheat plants. Molecules , 28(1), 241. doi: 10.3390/molecules28010241. Javaid, A., Khan, I. H., & Shoaib, A. (2023). Germination and growth response of Parthenium hysterophorus to lead toxicity. Plantarum , 5(1). Karim, Z., Qureshi, B. A., & Mumtaz, M. (2015). Geochemical baseline determination and pollution assessment of heavy metals in urban soils of Karachi, Pakistan. Ecological Indicators , 48, 358-364. doi: 10.1016/j.ecolind.2014.08.032. Khan, A., Javid, S., Muhmood, A., Mjeed, T., Niaz, A., & Majeed, A. (2013). Heavy metal status of soil and vegetables grown on peri-urban area of Lahore district. Soil and Environment , 32(1), 49-54. Khan, M. M., Islam, E., Irem, S., Akhtar, K., Ashraf, M. Y., Iqbal, J., & Liu, D. (2018). Pb-induced phytotoxicity in para grass ( Brachiaria mutica ) and Castorbean ( Ricinus communis L.): Antioxidant and ultrastructural studies. Chemosphere , 200, 257-265. doi: 10.1016/j.chemosphere.2018.02.101. LInDh, P., & LeMenkOVA, P. (2022). Soil contamination from heavy metals and persistent organic pollutants (PAH, PCB and HCB) in the coastal area of Västernorrland, Sweden. Gospodarka Surowcami Mineralnymi–Mineral Resources Management , 38(2), 147-168. doi: 10.24425/gsm.2022.141662. Lotfy, S., & Mostafa, A. (2014). Phytoremediation of contaminated soil with cobalt and chromium. Journal of Geochemical Exploration , 144, 367-373. doi: 10.1016/j.gexplo.2013.07.003. Ma, J., Saleem, M. H., Ali, B., Rasheed, R., Ashraf, M. A., Aziz, H., Ercisli, S., Riaz, S., Elsharkawy, M. M., & Hussain, I. (2022). Impact of foliar application of syringic acid on tomato ( Solanum lycopersicum L.) under heavy metal stress-insights into nutrient uptake, redox homeostasis, oxidative stress, and antioxidant defense. Frontiers in Plant Science , 13, 950120. doi: 10.3389/fpls.2022.950120. Malar, S., Manikandan, R., Favas, P. J., Sahi, S. V., & Venkatachalam, P. (2014). Effect of lead on phytotoxicity, growth, biochemical alterations and its role on genomic template stability in Sesbania grandiflora : a potential plant for phytoremediation. Ecotoxicology and environmental safety , 108, 249-257.doi: https://doi.org/10.1016/j.ecoenv.2014.05.018. Malik, R. N., Jadoon, W. A., & Husain, S. Z. (2010). Metal contamination of surface soils of industrial city Sialkot, Pakistan: a multivariate and GIS approach. Environmental geochemistry and health , 32, 179-191. doi: 10.1007/s10653-009-9274-1. Muhammad, S., Shah, M. T., & Khan, S. (2011). Health risk assessment of heavy metals and their source apportionment in drinking water of Kohistan region, northern Pakistan. Microchemical journal , 98(2), 334-343. doi: 10.1016/j.microc.2011.03.003. Mühlbachová, G. 2011. Soil microbial activities and heavy metal mobility in long-term contaminated soils after addition of EDTA and EDDS. Ecological Engineering . 37: 1064–1071. doi: 10.1016/j.ecoleng.2010.08.004. Nakano, Y., & Asada, K. (1981). Hydrogen peroxide is scavenged by ascorbate-specific peroxidase in spinach chloroplasts. Plant and cell physiology , 22(5), 867-880. doi: 10. 1093/oxfordjournals. pcp. a076 232. Naveed, S., Oladoye, P. O., & Alli, Y. A. (2023). Toxic heavy metals: A bibliographic review of risk assessment, toxicity, and phytoremediation technology. Sustainable Chemistry for the Environment , 100018. doi: 10.1016 /j.scenv. 2023.100018. Olsen, S. R. (1954). Estimation of available phosphorus in soils by extraction with sodium bicarbonate. US Department of Agriculture. Priya, A. K., Muruganandam, M., Ali, S. S., & Kornaros, M. (2023). Clean-Up of Heavy Metals from Contaminated Soil by Phytoremediation: A Multidisciplinary and Eco-Friendly Approach. Toxics , 11(5), 422. doi: 10.3390/toxics11050422. Pütter, J. (1974). Peroxidases. In Methods of enzymatic analysis (pp. 685-690). Academic Press. Qureshi, F. F., Ashraf, M. A., Rasheed, R., Ali, S., Hussain, I., Ahmed, A., & Iqbal, M. (2020). Organic chelates decrease phytotoxic effects and enhance chromium uptake by regulating chromium-speciation in castor bean ( Ricinus communis L.). Science of the Total Environment , 716, 137061. doi: 10.1016 /j.scitotenv. 2020.137061. Riazi, A., Matsuda, K., & Arslan, A. (1985). Water-stress induced changes in concentrations of proline and other solutes in growing regions of young barley leaves. Journal of Experimental Botany , 36(11), 1716-1725. doi: 10.1111/j.1399-3054.1992.tb08764.x. Saleem, M. H., Ali, S., Kamran, M., Iqbal, N., Azeem, M., Tariq Javed, M., Ali, Q., Zulqurnain Haider, M., Irshad, S., & Rizwan, M. (2020). Ethylenediaminetetraacetic acid (EDTA) mitigates the toxic effect of excessive copper concentrations on growth, gaseous exchange and chloroplast ultrastructure of Corchorus capsularis L. and improves copper accumulation capabilities. Plants , 9(6), 756. doi: 10.3390/plants9060756. Sidhu, G. P. S., Singh, H. P., Batish, D. R., & Kohli, R. K. (2016). Effect of lead on oxidative status, antioxidative response and metal accumulation in Coronopus didymus . Plant physiology and biochemistry , 105, 290-296. doi: 10.1016/j.plaphy.2016.05.019. Song, X., Zhou, G., Shi, L., Ahmad, I., Shi, X., Zhu, G., & Jiao, X. (2021). Comparative effects of salinity and drought on seed germination, seedling growth, photosynthetic productivity, pigments content and antioxidant enzymes of castor bean ( Ricinus communis ). Crop and Pasture Science , 72(7), 541-550. doi: 10.1071/CP20495. Steel, R. G. D., Torrie, J. H., and Dicky, D. A. (1997). Principles and Procedures of Statistics—A Biometrical Approach, 3rd Edn. New York, NY: McGraw-Hill. Teulat, B., Zoumarou-Wallis, N., Rotter, B., Ben Salem, M., Bahri, H., and This, D. (2003). QTL for relative water content in field-grown barley and their stability across Mediterranean environments. Theoretical and Applied Genetics .108, 181–188. doi: 10.1007/s00122-003-1417-7 Ullah, R., Bakht, J., Shafi, M., Iqbal, M., Khan, A., & Saeed, M. (2011). Phyto-accumulation of heavy metals by sunflower ( Helianthus annuus L.) grown on contaminated soil. African Journal of Biotechnology , 10(75), 17192-17198. doi: https://doi.org/10.5897/AJB11.1832. Ullah, S., Ali, R., Mahmood, S., Atif Riaz, M., & Akhtar, K. (2020). Differential growth and metal accumulation response of Brachiaria mutica and Leptochloa fusca on cadmium and lead contaminated soil. Soil and Sediment Contamination: An International Journal , 29(8), 844-859. doi: 10.1080/15320383.2020.1777935. Ullah, S., Mahmood, S., Ali, R., Khan, M. R., Akhtar, K., & Depar, N. (2021). Comparing chromium phyto-assessment in Brachiaria mutica and Leptochloa fusca growing on chromium polluted soil. Chemosphere , 269, 128728. doi: 10.1016/j.chemosphere.2020.128728. Ullah, S., Mahmood, T., Iqbal, Z., Naeem, A., Ali, R., & Mahmood, S. (2019). Phytoremediative potential of salt-tolerant grass species for cadmium and lead under contaminated nutrient solution. International journal of phytoremediation , 21(10), 1012-1018. doi: 10.1080/15226514.2019.1594683. Walkley, A., & Black, I. A. (1934). An examination of the Degtjareff method for determining soil organic matter, and a proposed modification of the chromic acid titration method. Soil science , 37(1), 29-38. Wang, L., Rinklebe, J., Tack, F. M., & Hou, D. (2021). A review of green remediation strategies for heavy metal contaminated soil. Soil Use and Management , 37(4), 936-963. Wani, Z. A., Ahmad, Z., Asgher, M., Bhat, J. A., Sharma, M., Kumar, A.,& Anjum, N. A. (2023). Phytoremediation of Potentially Toxic Elements: Role, Status and Concerns. Plants , 12(3), 429. doi: 10.3390/plants12030429. Yang, G., Rhodes, D., and Joly, R. J. (1996). Effect of high temperature on membrane stability and chlorophyll fluorescence in glycinebetaine-containing maize lines. Australian Journal of Plant Physiology. 23, 431–443. doi: 10.1071/PP9960437. Yang, J., Yang, J., & Huang, J. (2017). Role of co-planting and chitosan in phytoextraction of As and heavy metals by Pteris vittata and castor bean–a field case. Ecological engineering , 109, 35-40. doi: 10.1016/j.ecoleng.2017.09.001. Yang, Y., Liang, Y., Han, X., Chiu, T. Y., Ghosh, A., Chen, H., & Tang, M. (2016). The roles of arbuscular mycorrhizal fungi (AMF) in phytoremediation and tree-herb interactions in Pb contaminated soil. Scientific Reports , 6(1), 20469. doi:10.1038/srep20469. Zhou, G., Liu, C., Cheng, Y., Ruan, M., Ye, Q., Wang, R., Yao, Z., & Wan, H. (2022). Molecular evolution and functional divergence of stress-responsive Cu/Zn superoxide dismutases in plants. International Journal of Molecular Sciences , 23(13), 7082. doi: 10.3390/ijms23137082. Zulkernain, N. H., Basant, N., Ng, C. C., Kriti, Salari, M., & Mallick, S. (2023). Recovery of precious metals from e-wastes through conventional and phytoremediation treatment methods: a review and prediction. Journal of Material Cycles and Waste Managemet , 1-27. doi:10.1007/s10163-023-01717-5. Additional Declarations No competing interests reported. Cite Share Download PDF Status: Posted Version 1 posted You are reading this latest preprint version Research Square lets you share your work early, gain feedback from the community, and start making changes to your manuscript prior to peer review in a journal. As a division of Research Square Company, we’re committed to making research communication faster, fairer, and more useful. We do this by developing innovative software and high quality services for the global research community. Our growing team is made up of researchers and industry professionals working together to solve the most critical problems facing scientific publishing. Also discoverable on Platform About Our Team In Review Editorial Policies Advisory Board Help Center Resources Author Services Accessibility API Access RSS feed Manage Cookie Preferences © Research Square 2026 | ISSN 2693-5015 (online) Privacy Policy Terms of Service Do Not Sell My Personal Information {"props":{"pageProps":{"initialData":{"identity":"rs-3344644","acceptedTermsAndConditions":true,"allowDirectSubmit":true,"archivedVersions":[],"articleType":"Research Article","associatedPublications":[],"authors":[{"id":234270019,"identity":"c9bcfac4-e874-4e91-bc55-63759d5c455f","order_by":0,"name":"Sahar Naveed","email":"","orcid":"","institution":"Pakistan Institute of Engineering and Applied Sciences (PIEAS)","correspondingAuthor":false,"prefix":"","firstName":"Sahar","middleName":"","lastName":"Naveed","suffix":""},{"id":234270020,"identity":"cbad85dd-457c-476e-98af-cccdfb3b4d6d","order_by":1,"name":"Sajid Mahmood","email":"data:image/png;base64,iVBORw0KGgoAAAANSUhEUgAAAZAAAAAyAQMAAABI0h/eAAAABlBMVEX///8AAABVwtN+AAAACXBIWXMAAA7EAAAOxAGVKw4bAAAAvElEQVRIiWNgGAWjYBADOQYGHlLUH0hgMCZdS2ID0Vrkp50x/Pzxh036huNnDz74wGAnp9tAQIvB7RxjiQMJabkbzuQlG85gSDY2O0BIi3TuBqCWw7kbDuSYSfMwHEjcRkiL/OzczT+AWtINzr8hUgvD7dxtIFsSDG4Qa4vB7fxvFmfS0gxn3nhjbDjDgAi/yM9OS75RYWMjz3c+x/DBhwo7OYJa4EABrNKAWOVg6xpIUT0KRsEoGAUjCgAAaf5GDB/O4bQAAAAASUVORK5CYII=","orcid":"","institution":"Pakistan Institute of Engineering and Applied Sciences (PIEAS)","correspondingAuthor":true,"prefix":"","firstName":"Sajid","middleName":"","lastName":"Mahmood","suffix":""},{"id":234270021,"identity":"dd965252-7fe2-4740-8b67-dde0085ce159","order_by":2,"name":"Wajid Ishaque","email":"","orcid":"","institution":"Pakistan Institute of Engineering and Applied Sciences (PIEAS)","correspondingAuthor":false,"prefix":"","firstName":"Wajid","middleName":"","lastName":"Ishaque","suffix":""}],"badges":[],"createdAt":"2023-09-11 11:14:24","currentVersionCode":1,"declarations":"","doi":"10.21203/rs.3.rs-3344644/v1","doiUrl":"https://doi.org/10.21203/rs.3.rs-3344644/v1","draftVersion":[],"editorialEvents":[],"editorialNote":"","failedWorkflow":false,"files":[{"id":43658853,"identity":"c0d37e33-4012-41f8-a07c-64f716f7df50","added_by":"auto","created_at":"2023-09-25 23:05:30","extension":"jpg","order_by":1,"title":"Figure 1","display":"","copyAsset":false,"role":"figure","size":712547,"visible":true,"origin":"","legend":"\u003cp\u003e\u003cstrong\u003ePrincipal Component analysis showing relationship among castor genotypes and traits at various levels of Pb\u003c/strong\u003e\u003c/p\u003e","description":"","filename":"1.jpg","url":"https://assets-eu.researchsquare.com/files/rs-3344644/v1/43a92215d34be518b8175f1c.jpg"},{"id":44300052,"identity":"e0ac6ce7-f951-43b7-ba7c-002a462f6aa9","added_by":"auto","created_at":"2023-10-09 14:37:29","extension":"pdf","order_by":0,"title":"","display":"","copyAsset":false,"role":"manuscript-pdf","size":801293,"visible":true,"origin":"","legend":"","description":"","filename":"manuscript.pdf","url":"https://assets-eu.researchsquare.com/files/rs-3344644/v1/aad9216a-da56-410e-9cc1-56507ae1ddd8.pdf"}],"financialInterests":"No competing interests reported.","formattedTitle":"Differential growth and metal accumulation response of castor bean genotypes on a lead contaminated soil","fulltext":[{"header":"Introduction","content":"\u003cp\u003eIn the 21st century, pollution control is a major challenge due to the massive increase in pollutants produced by human activities. Among all, heavy metals and organic pollutants are known as two major factors behind soil pollution (LlnDh and LeMenkOVA, 2022). Lead is widely utilized for the manufacture of storage batteries, paints, alloy formation and casting etc (Khan et al., \u003cspan citationid=\"CR23\" class=\"CitationRef\"\u003e2018\u003c/span\u003e). The presence of Pb in the soil is hazardous to human health due to its long-lasting residual and chance of entry in the food chain (M\u0026uuml;hlbachov\u0026aacute;, \u003cspan citationid=\"CR30\" class=\"CitationRef\"\u003e2011\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eDifferent strategies are proposed for the remediation of heavy metal contaminated soils however, phytoremediation is considered cost-effective, environmental friendly, and easy to adopt technology with good public perception (Priya et al., \u003cspan citationid=\"CR34\" class=\"CitationRef\"\u003e2023\u003c/span\u003e). Phytoremediation, use of plants for environmental cleanup, is a promising remediation strategy. This technique is a safe and effective way to remove a variety of contaminants, with fewer negative side effects than traditional remediation strategies (Zulkernain et al., \u003cspan citationid=\"CR54\" class=\"CitationRef\"\u003e2023\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eCastor bean, \u003cem\u003eRicinus communis\u003c/em\u003e L., has good potential to grow well on heavy metal contaminated soils and accumulate these metals including Pb in aerial parts. Additionally, castor possesses enormous adaptive potential in diverse habitats including resistance against drought, salinity, and climate warming, hence, suitable for marginal lands. Moreover, castor is an important non-edible industrial oil crop with various non-food and industrial applications as being used in soap, cosmetics, pharmaceutical, paints and lubricants. Therefore, phytoremediation of Pb contaminated soils using castor crop may be an environmental friendly and safe option that could give economic benefits from contaminated soils as well (Song et al., \u003cspan citationid=\"CR40\" class=\"CitationRef\"\u003e2021\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eVarious studies have reported the potential of castor bean for the phytoremediation of heavy metal contaminated soils in Brazil (Andreazza et al., \u003cspan citationid=\"CR9\" class=\"CitationRef\"\u003e2013\u003c/span\u003e), China (Yang et al., \u003cspan citationid=\"CR51\" class=\"CitationRef\"\u003e2017\u003c/span\u003e) and India (Boda et al., \u003cspan citationid=\"CR11\" class=\"CitationRef\"\u003e2017\u003c/span\u003e). Heavy metal pollution is becoming an adverse problem in many cities of Pakistan including Karachi (Karim et al., \u003cspan citationid=\"CR21\" class=\"CitationRef\"\u003e2015\u003c/span\u003e), Faisalabad (Farid et al., \u003cspan citationid=\"CR16\" class=\"CitationRef\"\u003e2015\u003c/span\u003e), Lahore (Khan et al., \u003cspan citationid=\"CR22\" class=\"CitationRef\"\u003e2013\u003c/span\u003e), Kasur (Afzal et al., \u003cspan citationid=\"CR2\" class=\"CitationRef\"\u003e2014\u003c/span\u003e), Sialkot (Malik et al., \u003cspan citationid=\"CR28\" class=\"CitationRef\"\u003e2010\u003c/span\u003e), and Peshawar (Jan et al., \u003cspan citationid=\"CR18\" class=\"CitationRef\"\u003e2010\u003c/span\u003e). In a survey study, Afzal and coworkers (\u003cspan citationid=\"CR2\" class=\"CitationRef\"\u003e2014\u003c/span\u003e) determined the level of heavy metal contamination in groundwater and soil near the industrial area of Kasur. The survey results revealed that soil and groundwater in the study area are highly contaminated with all tested heavy metals specially chromium. Similarly, in case of soil, highest Pb concentration (1753 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e) was detected under mining activities from Kohistan region, Gilgit Baltistan province (Muhammad et al., \u003cspan citationid=\"CR29\" class=\"CitationRef\"\u003e2011\u003c/span\u003e).\u003c/p\u003e \u003cp\u003eThese findings indicate an alarming situation of heavy metals contamination of agricultural soils in the vicinities of industrial cities of Pakistan and demands urgent remedy for the removal of heavy metals from soils. Various lab and greenhouse studies reported the potential of different grasses (Ullah et al., \u003cspan citationid=\"CR46\" class=\"CitationRef\"\u003e2019\u003c/span\u003e), vegetables (Akhtar et al., \u003cspan citationid=\"CR6\" class=\"CitationRef\"\u003e2018\u003c/span\u003e) and oilseed crops (Qureshi et al., \u003cspan citationid=\"CR36\" class=\"CitationRef\"\u003e2020\u003c/span\u003e) for the phytoremediation of heavy metal contaminated soil. However, no mechanism based study is available regarding phytoremediation of Pb-contaminated soils using castor bean. Therefore, present study was designed to evaluate the growth, physiology and Pb uptake efficacy of castor genotypes for phytoremediation of Pb contaminated soils.\u003c/p\u003e"},{"header":"Materials and methods","content":"\u003cdiv id=\"Sec3\" class=\"Section2\"\u003e \u003ch2\u003eExperimental structure and treatment plan\u003c/h2\u003e \u003cp\u003eA pot experiment was conducted to evaluate the growth, physiological and phytoremediation response of different castor genotypes on Pb contaminated soil under wire house conditions at the Nuclear Institute for Agriculture and Biology (NIAB) Faisalabad, Pakistan with coordinates 31.4504 N and 73.1350 E. Seeds of five castor genotypes (NIAB Gold, NIAB Spineless, NIAB-2020, DS-30 and C-3) were collected from Plant Breeding and Genetics Division (PBGD), NIAB. Plastic pots (20 \u0026times; 22.5 cm) were filled with thoroughly mixed, air-dried and precisely sieved soil (5 kg) using 2 mm mesh. The well prepared soil was spiked with different concentrations of Pb (0, 100, 200, 400, and 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e soil) prior to 3 months of sowing to equilibrate the metal in the soil. For this, above stated Pb concentrations were firstly calculated and then applied in solution form using lead nitrate of Sigma Aldrich (purity\u0026thinsp;\u0026ge;\u0026thinsp;99.0%). Soil without any treatment of Pb was considered as control. After the accomplishment of the required time period, pre-soaked seeds were sown in each pot with three replications following completely randomized design (CRD) with factorial settings. Plants were grown under natural environment with average temperatures of 30\u0026ndash;35\u0026deg;C (night-day). The basal dose of fertilizer (NPK) was calculated and applied to each pot. Addition of nitrogen in soil through lead nitrate was adjusted while calculating the fertilizer dose (Ahmad, \u003cspan citationid=\"CR3\" class=\"CitationRef\"\u003e2010\u003c/span\u003e).\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec4\" class=\"Section2\"\u003e \u003ch2\u003ePhysicochemical analysis of the experimental soil\u003c/h2\u003e \u003cp\u003eSoil was collected in bulk from the experimental site of NIAB and categorized for different physicochemical analysis (Table\u0026nbsp;\u003cspan refid=\"Tab1\" class=\"InternalRef\"\u003e1\u003c/span\u003e). Bouyoucos hydrometer protocol was followed for the determination of soil texture (Lotfy and Mostafa, \u003cspan citationid=\"CR25\" class=\"CitationRef\"\u003e2014\u003c/span\u003e). Saturated paste was prepared to determine the pH of the soil using pH meter (ST-5000-OHAUS-USA) whereas soil extract was used to determine EC using EC meter (a-AB33EC, OHAUS, USA). Total nitrogen and available phosphorous were analyzed following Kjeldahl (Bremner, \u003cspan citationid=\"CR13\" class=\"CitationRef\"\u003e1960\u003c/span\u003e) and Olsen (\u003cspan citationid=\"CR33\" class=\"CitationRef\"\u003e1954\u003c/span\u003e) method, respectively. Organic matter was determined as described by Walkley and Black (\u003cspan citationid=\"CR47\" class=\"CitationRef\"\u003e1934\u003c/span\u003e). Total Pb in soil was determined by the method as described by Ullah et al. (\u003cspan citationid=\"CR44\" class=\"CitationRef\"\u003e2020\u003c/span\u003e).\u003c/p\u003e \u003cp\u003e \u003cdiv class=\"gridtable\"\u003e\u003ctable float=\"Yes\" id=\"Tab1\" border=\"1\"\u003e \u003ccaption language=\"En\"\u003e \u003cdiv class=\"CaptionNumber\"\u003eTable 1\u003c/div\u003e \u003cdiv class=\"CaptionContent\"\u003e \u003cp\u003ePhysiochemical analysis of the experimental soil\u003c/p\u003e \u003c/div\u003e \u003c/caption\u003e \u003ccolgroup cols=\"10\"\u003e \u003cdiv align=\"left\" class=\"colspec\" colname=\"c1\" colnum=\"1\"\u003e\u003c/div\u003e \u003cdiv align=\"left\" class=\"colspec\" colname=\"c2\" colnum=\"2\"\u003e\u003c/div\u003e \u003cdiv align=\"left\" class=\"colspec\" colname=\"c3\" colnum=\"3\"\u003e\u003c/div\u003e \u003cdiv align=\"left\" class=\"colspec\" colname=\"c4\" colnum=\"4\"\u003e\u003c/div\u003e \u003cdiv align=\"left\" class=\"colspec\" colname=\"c5\" colnum=\"5\"\u003e\u003c/div\u003e \u003cdiv align=\"left\" class=\"colspec\" colname=\"c6\" colnum=\"6\"\u003e\u003c/div\u003e \u003cdiv align=\"left\" class=\"colspec\" colname=\"c7\" colnum=\"7\"\u003e\u003c/div\u003e \u003cdiv align=\"left\" class=\"colspec\" colname=\"c8\" colnum=\"8\"\u003e\u003c/div\u003e \u003cdiv align=\"left\" class=\"colspec\" colname=\"c9\" colnum=\"9\"\u003e\u003c/div\u003e \u003cdiv align=\"left\" class=\"colspec\" colname=\"c10\" colnum=\"10\"\u003e\u003c/div\u003e \u003cthead\u003e \u003ctr\u003e \u003cth align=\"left\" colname=\"c1\"\u003e \u003cp\u003eSand (%)\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c2\"\u003e \u003cp\u003eSilt\u003c/p\u003e \u003cp\u003e(%)\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c3\"\u003e \u003cp\u003eClay\u003c/p\u003e \u003cp\u003e(%)\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c4\"\u003e \u003cp\u003eTexture\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c5\"\u003e \u003cp\u003epH\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c6\"\u003e \u003cp\u003eEC\u003c/p\u003e \u003cp\u003e(dS m\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c7\"\u003e \u003cp\u003eTotal N (%)\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c8\"\u003e \u003cp\u003eAvailable P (mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c9\"\u003e \u003cp\u003eO.M (%)\u003c/p\u003e \u003c/th\u003e \u003cth align=\"left\" colname=\"c10\"\u003e \u003cp\u003eTotal Pb\u003c/p\u003e \u003cp\u003e(mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e \u003c/th\u003e \u003c/tr\u003e \u003c/thead\u003e \u003ctbody\u003e \u003ctr\u003e \u003ctd align=\"left\" colname=\"c1\"\u003e \u003cp\u003e58\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c2\"\u003e \u003cp\u003e34.7\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c3\"\u003e \u003cp\u003e4.5\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c4\"\u003e \u003cp\u003eSandy loam\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c5\"\u003e \u003cp\u003e7.65\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c6\"\u003e \u003cp\u003e2.05\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c7\"\u003e \u003cp\u003e0.081\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c8\"\u003e \u003cp\u003e5.9\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c9\"\u003e \u003cp\u003e0.99\u003c/p\u003e \u003c/td\u003e \u003ctd align=\"left\" colname=\"c10\"\u003e \u003cp\u003eN.D\u003c/p\u003e \u003c/td\u003e \u003c/tr\u003e \u003c/tbody\u003e \u003c/colgroup\u003e \u003ctfoot\u003e \u003ctr\u003e\u003ctd colspan=\"10\"\u003eO.M\u0026thinsp;=\u0026thinsp;Organic matter, N.D\u0026thinsp;=\u0026thinsp;Not detected\u003c/td\u003e\u003c/tr\u003e \u003c/tfoot\u003e \u003c/table\u003e\u003c/div\u003e \u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec5\" class=\"Section2\"\u003e \u003ch2\u003eGas exchange parameters\u003c/h2\u003e \u003cp\u003eStomatal conductance, transpiration and photosynthetic rate of the plants were measured through Decagon (\u003cspan citationid=\"CR15\" class=\"CitationRef\"\u003e2011\u003c/span\u003e) method in the morning hours using a porometer (Lincor.Inc steady state porometer).\u003c/p\u003e \u003cdiv id=\"Sec6\" class=\"Section3\"\u003e \u003ch2\u003eEstimation of relative water content and electrolyte leakage\u003c/h2\u003e \u003cp\u003eRelative water content (RWC) of the castor bean genotypes were determined using the method as described by Teulat et al. (\u003cspan citationid=\"CR42\" class=\"CitationRef\"\u003e2003\u003c/span\u003e) whereas electrolyte leakage of castor genotypes were determined by the method as described by Yang et al. (\u003cspan citationid=\"CR50\" class=\"CitationRef\"\u003e1996\u003c/span\u003e).\u003c/p\u003e \u003c/div\u003e \u003c/div\u003e \u003cdiv id=\"Sec7\" class=\"Section2\"\u003e \u003ch2\u003ePlant growth parameters\u003c/h2\u003e \u003cp\u003ePlants were harvested after 2 months and data regarding plant height and shoot fresh weight were recorded. Roots were washed thoroughly with tap water using plastic mesh to remove the soil particles and then with deionized water to determine root fresh weight. Shoot and root samples were oven dried at 70\u003csup\u003e\u0026deg;\u003c/sup\u003eC for 72 hours to record dry weight.\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec8\" class=\"Section2\"\u003e \u003ch2\u003eDetermination of photosynthetic activity\u003c/h2\u003e \u003cp\u003eArnon (\u003cspan citationid=\"CR10\" class=\"CitationRef\"\u003e1949\u003c/span\u003e) protocol was opted to determine photosynthetic pigments in fresh leaves of castor genotypes.\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec9\" class=\"Section2\"\u003e \u003ch2\u003eDetermination of antioxidants enzymes\u003c/h2\u003e \u003cp\u003eAfter five weeks of germination, fresh samples (0.2 g) of castor leaves were ground and homogenized in 0.05 M phosphate buffer solution (pH 7.8). The homogenized mixture was filtered and centrifuged at 12,000 rpm for 10 minutes at 4\u003csup\u003e\u0026deg;\u003c/sup\u003eC.\u003c/p\u003e \u003cp\u003eSuperoxide dismutase activity was measured by following Giannopolitis and Ries (\u003cspan citationid=\"CR17\" class=\"CitationRef\"\u003e1977\u003c/span\u003e) protocol at 560 nm. P\u0026uuml;tter (\u003cspan citationid=\"CR35\" class=\"CitationRef\"\u003e1974\u003c/span\u003e) procedure was opted to determine peroxidase activity. The increase in absorbance due to the oxidation of guaiacol was measured spectrophotometrically at 470 nm. Catalase activity was determined by monitoring the reduction in the absorbance at 240 nm using the procedure as described by Aebi (\u003cspan citationid=\"CR1\" class=\"CitationRef\"\u003e1984\u003c/span\u003e). Ascorbate peroxidase (APX) activity was determined by the method as described by Nakano and Asada (\u003cspan citationid=\"CR31\" class=\"CitationRef\"\u003e1981\u003c/span\u003e).\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec10\" class=\"Section2\"\u003e \u003ch2\u003eDetermination of total soluble proteins, total soluble sugars and total phenolic contents\u003c/h2\u003e \u003cp\u003eTotal soluble protein (TSP) was determined as described by Bradford (\u003cspan citationid=\"CR12\" class=\"CitationRef\"\u003e1976\u003c/span\u003e). Total soluble sugars (TSS) were analyzed spectrophotometrically according to Riazi et al. (\u003cspan citationid=\"CR37\" class=\"CitationRef\"\u003e1985\u003c/span\u003e) procedure. Micro-colorimetric method was followed for the determination of total phenolic contents (TPC) (Ainsworth and Gillespie, \u003cspan citationid=\"CR5\" class=\"CitationRef\"\u003e2007\u003c/span\u003e).\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec11\" class=\"Section2\"\u003e \u003ch2\u003eLead concentration in shoot and root\u003c/h2\u003e \u003cp\u003eThe heavy metal analysis was performed following the protocol of Ullah et al. (\u003cspan citationid=\"CR44\" class=\"CitationRef\"\u003e2020\u003c/span\u003e) with some modifications. Ground and oven-dried shoot and root samples were digested with nitric acid and perchloric acid (8:2 v/v) on a hot plate until the sample become colorless. After cooling, the digested samples were diluted to 50 mL with distilled water and filtered through Whatman No. 42 filter paper. The metal analysis was carried out using atomic absorption spectroscopy (Analytikjena, contrAA 800D, Germany).\u003c/p\u003e \u003c/div\u003e \u003cdiv id=\"Sec12\" class=\"Section2\"\u003e \u003ch2\u003eStatistical analysis\u003c/h2\u003e \u003cp\u003eThe data obtained were analyzed using two-way analysis of variance (ANOVA) (Steel et al., \u003cspan citationid=\"CR41\" class=\"CitationRef\"\u003e1997\u003c/span\u003e) and the means were compared by applying the least significance difference test at p\u0026thinsp;\u0026le;\u0026thinsp;0.05. Data represent the mean of three replicates. The statistical analysis was conducted using the statistical software Statistix 8.1. Mean data of all parameters in the study were subjected to perform Principal Component Analysis (PCA) using XL-STAT software version 2014.\u003c/p\u003e \u003c/div\u003e"},{"header":"Results and Discussion","content":"\u003cdiv id=\"Sec14\" class=\"Section2\"\u003e\n\u003ch2\u003eEffect of Pb contamination on plant growth attributes\u003c/h2\u003e\n\u003cp\u003eThe analysis of variance showed a significant influence of Pb treatments on the growth attributes of different castor bean genotypes. Plant height was significantly decreased (\u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05) with the increasing concentrations of Pb in the soil. At 800 mg Pb kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e soil, NIAB-2020 showed better performance against Pb with an average height of 29.3 cm followed by DS-30 (28.0 cm) as compared to other genotypes. Shoot fresh biomass, root dry weight and shoot dry biomass were decreased due the presence of Pb. At 800 mg Pb kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e soil, the highest shoot fresh biomass up to 9.23 g plant\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e was observed in DS-30 followed by NIAB-2020 and C-3 i.e. 8.15 and 7.39 g plant\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e whereas maximum shoot dry weight and root dry weight i.e. 1.31 and 0.26 g plant\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e were recorded in NIAB-2020, respectively followed by DS-30 (Table\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e2\u003c/span\u003e).\u003c/p\u003e\n\u003cdiv class=\"gridtable\"\u003e\n\u003ctable id=\"Tab2\" border=\"1\"\u003e\u003ccaption\u003e\n\u003cdiv class=\"CaptionNumber\"\u003eTable 2\u003c/div\u003e\n\u003cdiv class=\"CaptionContent\"\u003e\n\u003cp\u003eEffect of different levels of lead contamination of soil on the agronomic parameters of different castor genotypes\u003c/p\u003e\n\u003c/div\u003e\n\u003c/caption\u003e\n\u003cthead\u003e\n\u003ctr\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003ePb\u003c/p\u003e\n\u003cp\u003e(mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e) soil\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eGenotypes\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eHT\u003c/p\u003e\n\u003cp\u003e(cm)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eFBM\u003c/p\u003e\n\u003cp\u003e(g plant\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eDBM\u003c/p\u003e\n\u003cp\u003e(g plant\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eRDW\u003c/p\u003e\n\u003cp\u003e(g plant\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e\n\u003c/th\u003e\n\u003c/tr\u003e\n\u003c/thead\u003e\n\u003ctbody\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e39.33 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e27.77 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.23 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.50 d\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e39.66 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e31.11 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.44 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.57 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e46.66 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e32.31 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.69 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.69 a\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e52.33 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e32.34 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.67 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.66 b\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e45.66 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e27.93 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.47 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.57 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e38.00 cde\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e24.92 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.93 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.42 f\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e38.33 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e24.95 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.09 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.48 e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e39.33 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e27.19 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.21 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.49 e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e38.66 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e26.92 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.19 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.49 e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e38.33 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e26.06 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.14 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.43 f\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e31.66 fg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e21.20 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.78 f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.37 j\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e33.33 f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e21.60 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.53 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.39 i\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e37.00 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e22.66 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.92 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.41 g\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e36.00 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e22.31 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.93 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.41 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e33.66 f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e21.30 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.52 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.40 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e400\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e30.00 ghi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e15.93 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.31 hij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.30 m\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e31.00 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e16.04 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.35 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.32 l\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e31.00 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e20.58 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.50 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.33 l\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e31.00 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e20.94 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.51 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.35 k\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e30.33 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.37 f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.43 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.32 l\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e800\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e23.66 k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e6.31 i\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.09 k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.13 p\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e22.00 k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e6.52 i\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.19 jk\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.19 o\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e29.33 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.15 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.31 hij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.26 n\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e28.00 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.23 h\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.29 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.20 o\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e26.00 j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e7.39 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.25 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.19 o\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"2\" align=\"left\"\u003e\n\u003cp\u003eLSD\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.25\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.44\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.12\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.02\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tbody\u003e\n\u003ctfoot\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"6\"\u003eData represent the mean of three replicates. Means within the same column having different letters are significantly different at \u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05 according to LSD. (Pb\u0026thinsp;=\u0026thinsp;lead); (NIAB-G\u0026thinsp;=\u0026thinsp;NIAB GOLD, NIAB-SPN\u0026thinsp;=\u0026thinsp;NIAB SPINELESS) and (Ht\u0026thinsp;=\u0026thinsp;Plant Height, FBM\u0026thinsp;=\u0026thinsp;Shoot fresh Biomass, DBM\u0026thinsp;=\u0026thinsp;Dry Biomass, RDW\u0026thinsp;=\u0026thinsp;Root dry weight).\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tfoot\u003e\n\u003c/table\u003e\n\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec15\" class=\"Section2\"\u003e\n\u003ch2\u003eEffect of Pb contamination of soil on physiological parameters\u003c/h2\u003e\n\u003cp\u003eTable\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e3\u003c/span\u003e illustrates the effect of Pb on the physiological parameters of different castor genotypes. The RWC of all genotypes were slightly affected with the increasing concentrations of Pb (\u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05). Comparing the varieties against each level of Pb, RWC showed a faint decreasing trend from 0 to 200 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e. At 800 mg Pb kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e soil, NIAB-2020 showed maximum retention of water in leaves (90%) followed by DS-30 (82%), NIAB Gold (80%), NIAB spineless (78%) and C-3 (70%) due to the production of osmolytes. Electrolyte leakage is the key response of plant against any abiotic stress. Electrolyte leakage was increased significantly with the increasing concentration of Pb in the soil (\u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05). At 800 mg Pb kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e soil, maximum electrolyte leakage was observed in NIAB spineless and NIAB Gold as compared to other genotypes.\u003c/p\u003e\n\u003cdiv class=\"gridtable\"\u003e\n\u003ctable id=\"Tab3\" border=\"1\"\u003e\u003ccaption\u003e\n\u003cdiv class=\"CaptionNumber\"\u003eTable 3\u003c/div\u003e\n\u003cdiv class=\"CaptionContent\"\u003e\n\u003cp\u003eEffect of different levels of lead contamination of soil on the physiological parameters of different castor genotypes\u003c/p\u003e\n\u003c/div\u003e\n\u003c/caption\u003e\n\u003cthead\u003e\n\u003ctr\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003ePb\u003c/p\u003e\n\u003cp\u003e(mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e) soil\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eGenotypes\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eRWC\u003c/p\u003e\n\u003cp\u003e(%)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eEL\u003c/p\u003e\n\u003cp\u003e(%)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eSC\u003c/p\u003e\n\u003cp\u003e(mmol m\u003csup\u003e\u0026minus;\u0026thinsp;2\u003c/sup\u003e s\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eTR\u003c/p\u003e\n\u003cp\u003e(mmol m\u003csup\u003e\u0026minus;\u0026thinsp;2\u003c/sup\u003e s\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003ePR\u003c/p\u003e\n\u003cp\u003e(umol m\u003csup\u003e\u0026minus;\u0026thinsp;2\u003c/sup\u003e s\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e\n\u003c/th\u003e\n\u003c/tr\u003e\n\u003c/thead\u003e\n\u003ctbody\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e99.00 a-d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.16 qr\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.36 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.55 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e383.53 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e99.40 abc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.42 rs\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e12.40 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.52 abc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e427.16 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e100.00 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e6.67 s\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e12.87 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.63 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e454.50 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e100.00 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e7.23 s\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e15.76 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.58 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e485.89 a\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e99.80 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.81 pq\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e12.20 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.52 abc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e346.52 de\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e95.62 a-f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e12.80 mno\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.64 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.44 b-e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e287.41 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e96.02 a-f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e13.85 lmn\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.91 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.45 b-e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e304.20 efg\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e98.80 a-d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.49 op\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.26 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.50 abc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e332.52 e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e97.93 a-e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e12.47 nop\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.26 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.49 a-d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e325.09 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e96.90 a-f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e14.49 klm\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.99 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.46 a-e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e314.71 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e93.37 a-f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e15.36 kl\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.38 fg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.31 efg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e242.76 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e93.82 a-f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e16.19 jk\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.39 fg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.32 d-g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e245.29 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e94.25 a-f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e14.75 kl\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.38 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.42 b-e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e251.62 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e95.01 a-f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e14.49 klm\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.78 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.42 b-e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e268.39 ghi\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e93.82 a-f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e17.19 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.62 efg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.37 c-f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e230.30 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e400\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e91.04 f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e37.68 f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e7.00 jk\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.06 hij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e193.41 jkl\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e91.87 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e24.54 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e7.68 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.11 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e183.64 klm\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e93.06 b-f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e17.36 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.85 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.14 ghi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e223.93 ijk\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e92.82 c-f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.25 i\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.09 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.20 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e194.73 jkl\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e92.58 def\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e20.24 h\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e7.92 i\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.05 h-k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e177.87 lm\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e800\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e80.40 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e109.92 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.51 m\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.92 jkl\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e140.63 mn\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e78.69 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e223.59 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e6.09 lm\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.88 kl\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e157.45 lmn\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e90.79 f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e81.85 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e6.65 kl\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.00 ijk\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e165.68 lm\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e82.26 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e102.36 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e6.80 kl\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.97 i-l\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e173.37 lm\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e70.59 h\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e106.26 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.44 m\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.81 l\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e119.66 n\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"2\" align=\"left\"\u003e\n\u003cp\u003eLSD\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e6.76\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.81\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.81\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.18\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e44.91\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tbody\u003e\n\u003ctfoot\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"7\"\u003eData represent the mean of three replicates. Means within the same column having different letters are significantly different at \u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05 according to LSD. (Pb\u0026thinsp;=\u0026thinsp;lead); (NIAB-G\u0026thinsp;=\u0026thinsp;NIAB GOLD, NIAB-SPN\u0026thinsp;=\u0026thinsp;NIAB SPINELESS) and (RWC\u0026thinsp;=\u0026thinsp;Relative Water content, EL\u0026thinsp;=\u0026thinsp;Electrolyte Leakage, SC\u0026thinsp;=\u0026thinsp;Stomatal Conductance, TR\u0026thinsp;=\u0026thinsp;Transpiration rate, PR\u0026thinsp;=\u0026thinsp;Photosynthesis rate).\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tfoot\u003e\n\u003c/table\u003e\n\u003c/div\u003e\n\u003cp\u003eObserving the gas exchange parameters, stomatal conductance, transpiration and photosynthetic rate were significantly reduced with the increasing concentrations of Pb (\u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05). A gradual decrease in stomatal conductance due to 100 to 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e Pb in soil disturbed the transpiration rate and photosynthesis in castor genotypes. At 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e, significant reduction in photosynthetic activity was observed in C-3 and NIAB Gold i.e. 119.6 and 140.63 mmol m\u003csup\u003e\u0026minus;\u0026thinsp;2\u003c/sup\u003e s\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e respectively, while highest photosynthetic activity was recorded in DS-30 and NIAB-2020.\u003c/p\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec16\" class=\"Section2\"\u003e\n\u003ch2\u003eEffects of Pb on leaf pigment contents\u003c/h2\u003e\n\u003cp\u003eThe effect of Pb on the pigment content of the castor genotypes resulted in significant decreasing trend (\u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05) with increasing metal stress. Interestingly, NIAB-2020 exhibited highest total chlorophyll and carotenoid content up to 8.61 and 3.59 mg g\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e respectively, as compared to other genotypes at 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e (Table\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e4\u003c/span\u003e).\u003c/p\u003e\n\u003cdiv class=\"gridtable\"\u003e\n\u003ctable id=\"Tab4\" border=\"1\"\u003e\u003ccaption\u003e\n\u003cdiv class=\"CaptionNumber\"\u003eTable 4\u003c/div\u003e\n\u003cdiv class=\"CaptionContent\"\u003e\n\u003cp\u003eEffect of different levels of lead contamination of soil on the photosynthetic pigments of different castor genotypes\u003c/p\u003e\n\u003c/div\u003e\n\u003c/caption\u003e\n\u003cthead\u003e\n\u003ctr\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003ePb\u003c/p\u003e\n\u003cp\u003e(mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e) soil\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eGenotypes\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eChl a\u003c/p\u003e\n\u003cp\u003emg g\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eChl b\u003c/p\u003e\n\u003cp\u003emg g\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eTotal Chl\u003c/p\u003e\n\u003cp\u003emg g\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eCarotenoids\u003c/p\u003e\n\u003cp\u003emg g\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e\u003c/p\u003e\n\u003c/th\u003e\n\u003c/tr\u003e\n\u003c/thead\u003e\n\u003ctbody\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.42 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.65 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.0 abc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.15 b\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.40 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.64 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.0 abc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.15 b\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.47 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.72 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.1 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.20 a\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.47 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.65 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.1 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.16 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.40 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.63 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.0 abc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.14 b\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.13 def\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.58 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.72 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.04 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.13 def\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.59 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.71 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.04 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.23 bcd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.62 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.85 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.05 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.35 abc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.59 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.94 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.05 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.19 cde\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.27 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.46 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.04 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.98 f-j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.24 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.23 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.01 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.02 e-i\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.23 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.24 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.02 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.11 d-g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.26 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.37 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.04 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.07 d-h\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.25 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.32 efg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.03 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.97 f-k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.23 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.20 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.96 d\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e400\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.89 h-l\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.16 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.05 h\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.71 f\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.86 i-l\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.88 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.74 i\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.90 e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.92 g-k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.19 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.11 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.95 de\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.97 f-k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.21 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.18 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.92 de\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.87 i-l\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.82 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.69 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.68 f\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e800\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.66 m-p\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.76 def\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.42 klm\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.50 h\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.72 l-o\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.76 def\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.47 jkl\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.58 g\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.84 i-m\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.77 def\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.61 ijk\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.59 g\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.82 j-m\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.76 def\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.58 ijk\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.59 g\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.78 k-n\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.75 def\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.54 i-l\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.58 g\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"2\" align=\"left\"\u003e\n\u003cp\u003eLSD\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.19\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.13\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.21\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.05\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tbody\u003e\n\u003ctfoot\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"6\"\u003eData represent the mean of three replicates. Means within the same column having different letters are significantly different at \u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05 according to LSD. (Pb\u0026thinsp;=\u0026thinsp;lead); (NIAB-G\u0026thinsp;=\u0026thinsp;NIAB GOLD, NIAB-SPN\u0026thinsp;=\u0026thinsp;NIAB SPINELESS) and (Chl a\u0026thinsp;=\u0026thinsp;Chlorophyll a, Chl b\u0026thinsp;=\u0026thinsp;Chlorophyll b, Total Chl\u0026thinsp;=\u0026thinsp;Total Chlorophyll).\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tfoot\u003e\n\u003c/table\u003e\n\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec17\" class=\"Section2\"\u003e\n\u003ch2\u003eEffect of Pb on the biochemical profile of castor bean\u003c/h2\u003e\n\u003cp\u003eResults revealed that in all genotypes, SOD and POD showed negative correlation whereas an increasing trend of CAT and APX were recorded with increasing concentrations of Pb (\u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05) as shown in Table \u003cspan class=\"InternalRef\"\u003e5\u003c/span\u003e. Interestingly, at 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e, highest CAT and APX activities were recorded in DS-30 (12.23 and 64.43 mM/g FW) followed by NIAB-2020 (12.13 and 64.31 mM/g FW), respectively (Table\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e5\u003c/span\u003e).\u003c/p\u003e\n\u003cdiv class=\"gridtable\"\u003e\n\u003ctable id=\"Tab5\" border=\"1\"\u003e\u003ccaption\u003e\n\u003cdiv class=\"CaptionNumber\"\u003eTable 5\u003c/div\u003e\n\u003cdiv class=\"CaptionContent\"\u003e\n\u003cp\u003eEffect of different levels of lead contamination of soil on the enzymatic antioxidants of different castor genotypes\u003c/p\u003e\n\u003c/div\u003e\n\u003c/caption\u003e\n\u003cthead\u003e\n\u003ctr\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003ePb\u003c/p\u003e\n\u003cp\u003e(mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e\n\u003cp\u003esoil\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eGenotypes\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eSOD\u003c/p\u003e\n\u003cp\u003e(U/g FW)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003ePOD\u003c/p\u003e\n\u003cp\u003e(mM/g FW)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eCAT\u003c/p\u003e\n\u003cp\u003e(mM/g FW)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eAPX\u003c/p\u003e\n\u003cp\u003e(mM/g FW)\u003c/p\u003e\n\u003c/th\u003e\n\u003c/tr\u003e\n\u003c/thead\u003e\n\u003ctbody\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2196.7 cde\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.19 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.86 i\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e30.73\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2300.7 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.29 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.86 j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e31.53 j\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3284.0 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e12.07 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.63 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e38.10 i\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2979.5 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.75 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.70 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e38.50 i\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2251.1 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.39 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.20 i\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e29.29 k\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1993.3 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e6.41 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.10 ghi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e40.77 h\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2045.8 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.97 fg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.60 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e40.53 h\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2142.2 cde\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e7.32 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.70 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e53.37 f\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2078.3 cde\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e7.46 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.83 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e53.40 f\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2032.5 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e7.01 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.10 ghi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e42.26 g\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1583.8 g-j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.39 ghi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e7.03 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e57.24 e\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1780.4 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.66 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.20 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e59.12 d\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1801.4 fg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.82 fg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.40 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e59.38 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1794.7 fg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.78 fg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.30 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e59.13 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1663.0 ghi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.30 g-j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e6.30 fg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e53.58 f\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e400\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1454.9 i-l\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.51 jk\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.80 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e59.75 bcd\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1548.4 ijk\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.58 ijk\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.40 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e59.64 bcd\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1568.5 h-k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.27 g-j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.20 bcd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e60.73 b\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1582.8 g-j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e5.14 g-j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.30 bcd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e60.70 b\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1520.8 ijk\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e4.90 hij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.13 bcd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e60.26 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e800\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1059.6 n\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.03 m\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.80 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e63.45 a\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1278.3 lmn\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.17 n\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.96 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e64.02 a\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1388.1 j-m\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.92 kl\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e12.13 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e64.31 a\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1357.5 klm\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.56 lm\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e12.23 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e64.43 a\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1182.8 mn\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.24 lm\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.33 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e63.45 a\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"2\" align=\"left\"\u003e\n\u003cp\u003eLSD\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e224.4\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.83\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.29\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.13\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tbody\u003e\n\u003ctfoot\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"6\"\u003eData represent the mean of three replicates. Means within the same column having different letters are significantly different at \u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05 according to LSD. (Pb\u0026thinsp;=\u0026thinsp;lead); (NIAB-G\u0026thinsp;=\u0026thinsp;NIAB GOLD, NIAB-SPN\u0026thinsp;=\u0026thinsp;NIAB SPINELESS) and (SOD\u0026thinsp;=\u0026thinsp;Superoxide dismutase, POD\u0026thinsp;=\u0026thinsp;Peroxidase, CAT\u0026thinsp;=\u0026thinsp;Catalase, APX\u0026thinsp;=\u0026thinsp;Ascorbate Peroxidase).\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tfoot\u003e\n\u003c/table\u003e\n\u003c/div\u003e\n\u003cp\u003eA vigorous increase in TSS and TPC from 200 to 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e were observed in all castor genotypes. At 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e, NIAB-2020, DS-30 and NIAB Spineless showed an equal production of soluble sugars of 18.6 mg g\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e. With reference to phenolic contents, NIAB-2020 produced two times more phenolic contents up to 0.49 mg g\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e as compared to other genotypes. Total soluble proteins showed negative relation to Pb concentrations. At 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e, DS-30 produced 8.44 mg g\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e total soluble proteins followed by NIAB-2020, NIAB spineless, NIAB Gold and C-3 (Table\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e6\u003c/span\u003e).\u003c/p\u003e\n\u003cdiv class=\"gridtable\"\u003e\n\u003ctable id=\"Tab6\" border=\"1\"\u003e\u003ccaption\u003e\n\u003cdiv class=\"CaptionNumber\"\u003eTable 6\u003c/div\u003e\n\u003cdiv class=\"CaptionContent\"\u003e\n\u003cp\u003eEffect of different levels of lead contamination on the non-enzymatic antioxidants of different castor genotypes\u003c/p\u003e\n\u003c/div\u003e\n\u003c/caption\u003e\n\u003cthead\u003e\n\u003ctr\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003ePb\u003c/p\u003e\n\u003cp\u003e(mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eGenotypes\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eTSP\u003c/p\u003e\n\u003cp\u003e(mg/g)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eTSS\u003c/p\u003e\n\u003cp\u003e(mg/g)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eTPC\u003c/p\u003e\n\u003cp\u003e(mg/g)\u003c/p\u003e\n\u003c/th\u003e\n\u003c/tr\u003e\n\u003c/thead\u003e\n\u003ctbody\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.33 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e13.99 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.14 k\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.60 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e13.99 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.14 k\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.90 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e14.01 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.15 k\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e12.10 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e14.09 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.15 k\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.60 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e14.01 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.14 k\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.00 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e14.09 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.15 k\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e10.03 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e14.12 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.19 j\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.23 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e14.20 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.21 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.25 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e14.20 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.20 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e11.23 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e14.12 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.19 j\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.02 efg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.42 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.21 ghi\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.04 efg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.42 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.22 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.94 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.44 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.23 g\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.66 cde\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.44 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.23 g\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.26 def\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.42 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.21 ghi\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e400\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.48 ghi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.44 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.28 f\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.71 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.54 abc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.30 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.90 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.54 abc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.31 de\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e9.01 efg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.59 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.31 de\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.90 fgh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.54 abc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.31 de\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e800\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e7.59 j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.59 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.32 d\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e7.83 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.69 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.34 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.21 hij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.69 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.49 a\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e8.44 ghi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.69 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.38 b\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e6.77 k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e18.59 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.34 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"2\" align=\"left\"\u003e\n\u003cp\u003eLSD\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.68\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.15\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.02\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tbody\u003e\n\u003ctfoot\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"5\"\u003eData represent the mean of three replicates. Means within the same column having different letters are significantly different at \u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05 according to LSD. (Pb\u0026thinsp;=\u0026thinsp;lead); (NIAB-G\u0026thinsp;=\u0026thinsp;NIAB GOLD, NIAB-SPN\u0026thinsp;=\u0026thinsp;NIAB SPINELESS) and (TSS\u0026thinsp;=\u0026thinsp;Total Soluble sugars, TSP\u0026thinsp;=\u0026thinsp;Total Soluble Proteins, TPC\u0026thinsp;=\u0026thinsp;Total Phenolic contents).\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tfoot\u003e\n\u003c/table\u003e\n\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec18\" class=\"Section2\"\u003e\n\u003ch2\u003eLead uptake in castor genotypes\u003c/h2\u003e\n\u003cp\u003eResults have shown a significant increase in the concentration of Pb in plant tissues of all castor genotypes (\u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05). Elemental analysis have shown higher concentration of Pb in roots as compared to shoots. At 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e, highest concentration of Pb in the roots were recorded in NIAB-2020 (302.0 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e) followed by DS-30 (299.3 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e). The highest translocation factor of 0.99 was observed in NIAB-2020. The bioconcentration factor of roots (BCFroot) increased with the increasing concentration of Pb as compared to bioconcentration factor of shoots (BCFshoot). At 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e, NIAB-2020 showed the maximum value of 3.59 followed by DS-30 (3.29) (Table\u0026nbsp;\u003cspan class=\"InternalRef\"\u003e7\u003c/span\u003e).\u003c/p\u003e\n\u003cdiv class=\"gridtable\"\u003e\n\u003ctable id=\"Tab7\" border=\"1\"\u003e\u003ccaption\u003e\n\u003cdiv class=\"CaptionNumber\"\u003eTable 7\u003c/div\u003e\n\u003cdiv class=\"CaptionContent\"\u003e\n\u003cp\u003eDetermination of different levels of lead in the shoot and root of different castor genotypes\u003c/p\u003e\n\u003c/div\u003e\n\u003c/caption\u003e\n\u003cthead\u003e\n\u003ctr\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003ePb\u003c/p\u003e\n\u003cp\u003e(mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eGenotypes\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eShoot\u003c/p\u003e\n\u003cp\u003e(mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eRoot\u003c/p\u003e\n\u003cp\u003e(mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e)\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eTF\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eBCFshoots\u003c/p\u003e\n\u003c/th\u003e\n\u003cth align=\"left\"\u003e\n\u003cp\u003eBCFroots\u003c/p\u003e\n\u003c/th\u003e\n\u003c/tr\u003e\n\u003c/thead\u003e\n\u003ctbody\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e0\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eN/D\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e100\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e28.67 o\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e43.67 o\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.63 m\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.93 o\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.38 l\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e29.83 o\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e50.33 n\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.64 lm\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.94 o\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.71 k\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e33.67 n\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e51.50 n\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.65 klm\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.20 mn\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.81 k\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e37.00 m\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e50.50 n\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.66 kl\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.30 m\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.80 k\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e32.00 n\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e43.67 o\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.64 klm\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.09 n\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.41 l\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e200\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e81.00 j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e90.33 m\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.68 i\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.86 k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.45 j\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e78.33 k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e99.67 kl\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.68 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.75 kl\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.64 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e83.67 i\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e103.00 j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.71 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.07 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.70 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e82.00 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e100.67 k\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.69 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.05 j\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.66 h\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e71.00 l\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e98.00 l\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.66 jk\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.70 l\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.52 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e400\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e122.67 h\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e190.00 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.72 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.12 ij\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.87 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e123.00 h\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e189.00 i\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.78 f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.18 hi\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.82 fg\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e135.00 f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e196.00 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.81 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.39 fg\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.92 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e139.00 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e199.00 f\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.86 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.50 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.96 de\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e125.67 g\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e191.67 h\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.81e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.29 gh\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.88 ef\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd rowspan=\"5\" align=\"left\"\u003e\n\u003cp\u003e800\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-G\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e252.00 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e288.00 e\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.86 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.58 de\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.98 de\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB-SPN\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e253.00 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e290.00 d\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.89 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.68 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.05 cd\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eNIAB- 2020\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e299.23 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e302.00 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.99 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.92 a\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.59 a\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eDS-30\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e289.17 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e299.33 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.96 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.89 ab\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.29 b\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003eC-3\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e272.80 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e293.00 c\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.94 b\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.78 bc\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e3.16 c\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"2\" align=\"left\"\u003e\n\u003cp\u003eLSD\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e2.06\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e1.71\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.02\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.12\u003c/p\u003e\n\u003c/td\u003e\n\u003ctd align=\"left\"\u003e\n\u003cp\u003e0.12\u003c/p\u003e\n\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tbody\u003e\n\u003ctfoot\u003e\n\u003ctr\u003e\n\u003ctd colspan=\"7\"\u003eData represent the mean of three replicates. Means within the same column having different letters are significantly different at \u003cem\u003ep\u003c/em\u003e\u0026thinsp;\u0026le;\u0026thinsp;0.05 according to LSD. (Pb\u0026thinsp;=\u0026thinsp;lead); (NIAB-G\u0026thinsp;=\u0026thinsp;NIAB GOLD, NIAB-SPN\u0026thinsp;=\u0026thinsp;NIAB SPINELESS) and (N/D\u0026thinsp;=\u0026thinsp;Not Detected, TF\u0026thinsp;=\u0026thinsp;Translocation factor, BCF\u0026thinsp;=\u0026thinsp;Bio concentration factor).\u003c/td\u003e\n\u003c/tr\u003e\n\u003c/tfoot\u003e\n\u003c/table\u003e\n\u003c/div\u003e\n\u003c/div\u003e\n\u003cdiv id=\"Sec19\" class=\"Section2\"\u003e\n\u003ch2\u003ePrincipal component analysis\u003c/h2\u003e\n\u003cp\u003ePrincipal component analysis was performed to analyze the visual comparison of castor genotypes, and to collect information about the inter-relationship between variables at different levels of Pb as shown in Fig.\u0026nbsp;1. Morpho-physiological parameters, pigment content, antioxidant activities, osmolytes, and Pb uptake were investigated using PCA. Biplot showed that among 8 principal components, 4 have Eigenvalues\u0026thinsp;\u0026gt;\u0026thinsp;1, while remaining components have not been discussed due to Eigenvalues\u0026thinsp;\u0026lt;\u0026thinsp;1.\u003c/p\u003e\n\u003cp\u003eAt 0 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e, EL showed strong association with NIAB Gold, NIAB Spineless and C-3 whereas RWW, TF, TSS, CAT, DBM, RWC, FBM, Pb in root and shoot, chlorophyll a, total chlorophyll and bioconcentration factor in roots were linked to DS-30. Ascorbate peroxidase, SC, PR, SOD, TPC, and chlorophyll \u003cem\u003eb\u003c/em\u003e co-occurred with NIAB-2020 (Fig.\u0026nbsp;1-a). It have been observed that with the increase in Pb contamination in soil, major agronomic, physiological and biochemical parameters were strongly connected to DS-30 and NIAB-2020 as compared to NIAB Gold, NIAB Spineless and C-3. At 100 and 200 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e, CAT, TPC, RWC, TSS, APX, TSP, SOD and POD along with other parameters aids in the survival of DS-30 and NIAB-2020 under Pb stress (Fig.\u0026nbsp;1-b, c). Similar responses were observed at 400 and 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e in DS-30 and NIAB-2020 (Fig.\u0026nbsp;1-d, e).\u003c/p\u003e\n\u003cp\u003eLead exposure have a variety of negative effects on plant growth including physiological disruptions, decreased biomass production, membrane and structural damage and reduced pigment contents. The extent of these effects depends on the type of plant and the concentration of Pb in soil. Our present study have shown that plant height, shoot fresh weight, shoot dry weight and root dry weight in all castor genotypes were decreased due to Pb contamination in soil. Physiological parameters including RWC, EL, SC, TR and PR were also decreased. Photosynthetic pigments including chlorophyll a, b and carotenoids were reduced due to Pb stress.\u003c/p\u003e\n\u003cp\u003ePlant height was decreased with the increasing concentrations of Pb. Similar trend was reported in \u003cem\u003eBrachiaria mutica\u003c/em\u003e (Ullah et al., \u003cspan class=\"CitationRef\"\u003e2021\u003c/span\u003e). This suggests that lead interfered more strongly with the plant's metabolic processes over time. It has been observed that shoot fresh and dry biomass declined in \u003cem\u003eParthenium hysterophorus\u003c/em\u003e (Javaid et al., \u003cspan class=\"CitationRef\"\u003e2023\u003c/span\u003e) due to Pb contamination. Comparable outcomes in terms of shoot fresh and dry biomass in the present study under higher level of Pb contamination were recorded in castor bean. Likewise, a declining trend was observed in root dry weight with increasing levels of Pb contamination. Similar effects of Pb contamination on root dry weight have also been reported in \u003cem\u003eSolanum lycopersicum\u003c/em\u003e (Ma et al., \u003cspan class=\"CitationRef\"\u003e2022\u003c/span\u003e) and \u003cem\u003eSesamum indicum\u003c/em\u003e (Naveed et al., \u003cspan class=\"CitationRef\"\u003e2023\u003c/span\u003e).\u003c/p\u003e\n\u003cp\u003eRelative water content (RWC) is an important parameter in water relation studies. Upon exposure to Pb stress, relative water content was decreased with the increasing Pb concentrations. Previous studies on \u003cem\u003eHelianthus annuus\u003c/em\u003e also showed the similar results (Al-Jobori and Kadhim, \u003cspan class=\"CitationRef\"\u003e2019\u003c/span\u003e). In castor bean, electrolyte leakage was increased with the increasing Pb concentrations in soil. Our findings are consistent with the previous studies which reported that exposure to Ni and Pb can increase electrolyte leakage in \u003cem\u003eCoronopus didymus\u003c/em\u003e (Sidhu et al., \u003cspan class=\"CitationRef\"\u003e2016\u003c/span\u003e). Observing the gas exchange attributes, stomatal conductance, transpiration and photosynthetic rate were declined with the increasing concentrations of Pb in soil as reported in \u003cem\u003eCorchorus capsularis\u003c/em\u003e (Saleem et al., \u003cspan class=\"CitationRef\"\u003e2020\u003c/span\u003e). Exposure to lead (Pb) can have a significant impact on the amount and type of pigments synthesis in plants. Different studies on tomato (Ma et al., \u003cspan class=\"CitationRef\"\u003e2022\u003c/span\u003e) supported the results recorded in castor bean under Pb contamination. The concentrations of chlorophyll and carotenoids were reduced as Pb disrupted the structure and function of enzymes involved in chlorophyll synthesis and directly interact with the components of photosystem II (PSII).\u003c/p\u003e\n\u003cp\u003eSuperoxide dismutase is especially important in providing first-line resistance to the toxic impact of ROS (Zhou et al., \u003cspan class=\"CitationRef\"\u003e2022\u003c/span\u003e). In general, antioxidant activity is promoted under lower levels of heavy metal stress, but it decreases at higher levels of stress. In this study, SOD and POD was decreased with the increasing concentrations of Pb. The decline in SOD and POD in our study may be assigned to Pb stress that damaged the antioxidant enzymatic systems. Similarly, decreasing trend of SOD and POD has been observed in \u003cem\u003eBrachiaria mutica\u003c/em\u003e. Conversely, CAT and APX were increased upon exposure to Pb stress. For example, in \u003cem\u003eE. argyi\u003c/em\u003e, a concentration-dependent increase in CAT activity was observed in response to Pb toxicity. This suggests that CAT activity may be one of the mechanisms by which castor bean plants detoxify Pb. The increase in CAT activity can be explained by an increase in its substrate (H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u003c/sub\u003e) and could be an adaptive mechanism of the plant to balance H\u003csub\u003e2\u003c/sub\u003eO\u003csub\u003e2\u003c/sub\u003e level (Khan et al., \u003cspan class=\"CitationRef\"\u003e2018\u003c/span\u003e).\u003c/p\u003e\n\u003cp\u003eThe production of total soluble proteins in castor bean has been decreased under Pb stress. Previously, under Pb stress \u003cem\u003eBrassica rapa\u003c/em\u003e have shown a decline in concentration of TSP (Ahmad et al., 2023). Results showed that TPC have been increased under Pb stress. Similar increase in phenol content has been reported in winter wheat plants under Pb contamination (Jańczak-Pieniążek et al., \u003cspan class=\"CitationRef\"\u003e2022\u003c/span\u003e). Studies have shown that the concentration of soluble sugars in plants increased markebly when exposed to stress. This is a possible mechanism that plants use to mitigate the negative effects of Pb stress. Our findings have shown an abrupt increase in the concentration of total soluble sugars from 200\u0026ndash;800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e. In a previous study, \u003cem\u003ePhaseolus vulgaris\u003c/em\u003e showed significant increase in reducing sugars under Pb contamination (Aldoobie et al., 2013).\u003c/p\u003e\n\u003cp\u003eCastor bean has been well known for its hyperaccumulating efficiency to uptake various heavy metals from soil. Results have shown that accumulation of Pb was higher in roots of castor as compared to shoots. The plant's extensive root system aids in binding and immobilizing lead ions, thereby reducing their movement in the soil profile (Wani et al., \u003cspan class=\"CitationRef\"\u003e2023\u003c/span\u003e). The accumulation of lead is known to increase in a concentration-dependent manner, but its translocation from root to shoot is low in plants such as \u003cem\u003eZea mays\u003c/em\u003e (Yang et al., \u003cspan class=\"CitationRef\"\u003e2016\u003c/span\u003e), \u003cem\u003eCannabis sativa\u003c/em\u003e (Ćaćić et al., \u003cspan class=\"CitationRef\"\u003e2019\u003c/span\u003e), \u003cem\u003eHelianthus annuus\u003c/em\u003e (Ullah et al., \u003cspan class=\"CitationRef\"\u003e2011\u003c/span\u003e), \u003cem\u003eBrachiaria mutica\u003c/em\u003e (Khan et al., \u003cspan class=\"CitationRef\"\u003e2018\u003c/span\u003e), and \u003cem\u003eSesbania grandiflora\u003c/em\u003e (Malar et al., \u003cspan class=\"CitationRef\"\u003e2014\u003c/span\u003e). Hence, phytoremediation using castor bean could be a promising technology for the removal of heavy metals from contaminated soil. This can help to certify the security of agricultural products, such as fruits and vegetables which are an important part of the human food.\u003c/p\u003e\n\u003c/div\u003e"},{"header":"Conclusion","content":"\u003cp\u003eThe current study has revealed that Pb toxicity negatively affects the agronomic and physiological parameters, pigment content as well as some osmolytes in castor genotypes due to ROS production and reduced antioxidant capacities. Hyper-Accumulation of Pb was higher in castor roots as compared to shoots. NIAB-2020 and DS-30 showed the better performance as compared to NIAB Gold, NIAB Spineless and C-3. Thus, castor bean has demonstrated its efficiency in multiple phytoremediation mechanisms, making it a versatile tool for remediating lead-contaminated soils.\u003c/p\u003e"},{"header":"Declarations","content":"\u003cp\u003e\u003cstrong\u003eAcknowledgments\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eAuthors are extremely obliged to NIAB-C, PIEAS, for providing the permission and analytical facilities to carry out the PhD study and complete the research.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eEthics approval and consent to participate\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eAll authors have read, understood, and have complied as applicable with the statement on \u0026quot;Ethical responsibilities of Authors\u0026quot; as found in the Instructions for Authors and are aware that with minor exceptions, no changes can be made to authorship once the paper is submitted. Moreover, all authors consent to participate.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eAvailability of data and material\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eThe authors confirm that the data supporting the findings of this study are available within the article.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eCompeting interests\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eAuthors declare no competing interest.\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eFunding\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eThis research did not receive any specific grant from funding agencies in the public, commercial, or Not for profit sectors\u003c/p\u003e\n\u003cp\u003e\u003cstrong\u003eAuthors contributions\u003c/strong\u003e\u003c/p\u003e\n\u003cp\u003eSahar Naveed: literature review, conceptualization, methodology, modeling, result analysis, conclusion, and writing the original manuscript. Sajid Mahmood: conceptualization, supervision/guidance, and reviewed original manuscript. Wajid Ishaque: technical support and helped in concluding the manuscript.\u003c/p\u003e"},{"header":"References","content":"\u003col\u003e\n\u003cli\u003eAebi, H.,1984. Catalase in vitro. Methods Enzymol.105, 121\u0026ndash;126. doi: 10.1016/S0076 6879(84) 0 5016-3.\u003c/li\u003e\n\u003cli\u003eAfzal, M., Shabir, G., Iqbal, S., Mustafa, T., Khan, Q. M., \u0026amp; Khalid, Z. M. (2014). Assessment of heavy metal contamination in soil and groundwater at leather industrial area of Kasur, Pakistan. \u003cem\u003eCLEAN\u0026ndash;Soil, Air, Water\u003c/em\u003e, 42(8), 1133-1139. doi: 10.1002/clen.201100715.\u003c/li\u003e\n\u003cli\u003eAhmad, F. (2010). \u003cem\u003eLeptochloa fusca\u003c/em\u003e cultivation for utilization of salt-affected soil and water resources in Cholistan Desert. \u003cem\u003eSociedade \u0026amp; Natureza\u003c/em\u003e, 22, 141-149. doi.org/10.1590/S1982-45132010000100010.\u003c/li\u003e\n\u003cli\u003eAhmed, S., Khan, M., \u0026amp; Sardar, R. (2023). Glutathione primed seed improved lead-stress tolerance in \u003cem\u003eBrassica rapa\u003c/em\u003e L. through modulation of physio-biochemical attributes and nutrient uptake. \u003cem\u003eInternational Journal of Phytoremediation\u003c/em\u003e, 1-11. doi: 10.1080/15226514.2023.2178380.\u003c/li\u003e\n\u003cli\u003eAinsworth, E. A., \u0026amp; Gillespie, K. M. (2007). Estimation of total phenolic content and other oxidation substrates in plant tissues using Folin\u0026ndash;Ciocalteu reagent. \u003cem\u003eNature protocols\u003c/em\u003e, 2(4), 875-877. doi: 10.1038/nprot.2007.102.\u003c/li\u003e\n\u003cli\u003eAkhtar, M. J., Ullah, S., Ahmad, I., Rauf, A., Nadeem, S. M., Khan, M. Y., \u0026amp; Bulgariu, L. (2018). Nickel phytoextraction through bacterial inoculation in \u003cem\u003eRaphanus sativus\u003c/em\u003e. \u003cem\u003eChemosphere\u003c/em\u003e, 190, 234-242. doi:10.1016/j.chemosphere.2017.09.136.\u003c/li\u003e\n\u003cli\u003eAldoobie, N. F., \u0026amp; Beltagi, M. S. (2013). Physiological, biochemical and molecular responses of common bean (\u003cem\u003ePhaseolus vulgaris\u003c/em\u003e L.) plants to heavy metals stress. \u003cem\u003eAfrican Journal of Biotechnology\u003c/em\u003e, 12(29), pp. 4614-4622. doi: 10.5897/AJB2013.12387.\u003c/li\u003e\n\u003cli\u003eAl-Jobori, K. M., \u0026amp; Kadhim, A. K. (2019). Evaluation of sunflower (\u003cem\u003eHelianthus annuus\u003c/em\u003e L.) for phytoremediation of lead contaminated soil. \u003cem\u003eJournal of Pharmaceutical Sciences and Research\u003c/em\u003e, 11(3), 847-854. doi: 10.5539/ep.v3n2p65.\u003c/li\u003e\n\u003cli\u003eAndreazza, R., Bortolon, L., Pieniz, S., \u0026amp; Camargo, F. A. O. (2013). Use of high-yielding bioenergy plant castor bean (\u003cem\u003eRicinus communis\u003c/em\u003e L.) as a potential phytoremediator for copper-contaminated soils. \u003cem\u003ePedosphere\u003c/em\u003e, 23(5), 651-661. doi: 10.1016/S1002-0160(13)60057-0.\u003c/li\u003e\n\u003cli\u003eArnon, D. I. (1949). Copper enzymes in isolated chloroplasts. Polyphenoloxidase in Beta vulgaris. \u003cem\u003ePlant physiology\u003c/em\u003e, 24(1), 1. doi: 10.1104/pp.24.1.1.\u003c/li\u003e\n\u003cli\u003eBoda, R. K., Majeti, N. V. P., \u0026amp; Suthari, S. (2017). \u003cem\u003eRicinus communis\u003c/em\u003e L.(castor bean) as a potential candidate for revegetating industrial waste contaminated sites in peri-urban Greater Hyderabad: remarks on seed oil. \u003cem\u003eEnvironmental Science and Pollution Research\u003c/em\u003e, 24, 19955-19964. doi: 10.1007/s11356-017-9654-5.\u003c/li\u003e\n\u003cli\u003eBradford, M. M. (1976). A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein-dye binding. \u003cem\u003eAnalytical biochemistry\u003c/em\u003e, 72(1-2), 248-254. doi: 10.1016/0003-2697(76)90527-3.\u003c/li\u003e\n\u003cli\u003eBremner, J. (1960). Determination of nitrogen in soil by the Kjeldahl method. \u003cem\u003eThe Journal of Agricultural Science\u003c/em\u003e, 55(1), 11-33. doi:10.1017/S0021859600021572.\u003c/li\u003e\n\u003cli\u003eĆaćić, M., Perčin, A., Zgorelec, Ž., \u0026amp; Kisić, I. (2019). Evaluation of heavy metals accumulation potential of hemp (\u003cem\u003eCannabis sativa\u003c/em\u003e L.). \u003cem\u003eJournal of Central European Agriculture\u003c/em\u003e, 20(2), 700-711.\u003c/li\u003e\n\u003cli\u003eDecagon (2011). Leaf Porometer Upgraded Model Sc-1. Pullman, WA: Decagon Devices, Inc.\u003c/li\u003e\n\u003cli\u003eFarid, G., Sarwar, N., Saifullah, A. A., Ghafoor, A., \u0026amp; Rehman, M. (2015). Heavy metals (Cd, Ni and Pb) contamination of soils, plants and waters in Madina town of Faisalabad metropolitan and preparation of GIS based maps. \u003cem\u003eAdvances in Crop Science and Technology\u003c/em\u003e, 4(2), 693-706. doi: 10.4172/2329-8863.1000199.\u003c/li\u003e\n\u003cli\u003eGiannopolitis, C. N., \u0026amp; Ries, S. K. (1977). Superoxide dismutases: I. Occurrence in higher plants. \u003cem\u003ePlant physiology\u003c/em\u003e, 59(2), 309-314. doi: 10.1104/pp.59.2.309.\u003c/li\u003e\n\u003cli\u003eJan, F. A., Ishaq, M., Ihsanullah, I., \u0026amp; Asim, S. M. (2010). Multivariate statistical analysis of heavy metals pollution in industrial area and its comparison with relatively less polluted area: a case study from the City of Peshawar and district Dir Lower. \u003cem\u003eJournal of hazardous materials\u003c/em\u003e, 176(1-3), 609-616. doi: 10.1016/j.jhazmat.2009.11.073.\u003c/li\u003e\n\u003cli\u003eJańczak-Pieniążek, M., Cichoński, J., Michalik, P., \u0026amp; Chrzanowski, G. (2022). Effect of heavy metal stress on phenolic compounds accumulation in winter wheat plants. \u003cem\u003eMolecules\u003c/em\u003e, 28(1), 241. doi: 10.3390/molecules28010241.\u003c/li\u003e\n\u003cli\u003eJavaid, A., Khan, I. H., \u0026amp; Shoaib, A. (2023). Germination and growth response of \u003cem\u003eParthenium hysterophorus\u003c/em\u003e to lead toxicity. \u003cem\u003ePlantarum\u003c/em\u003e, 5(1). \u003c/li\u003e\n\u003cli\u003eKarim, Z., Qureshi, B. A., \u0026amp; Mumtaz, M. (2015). Geochemical baseline determination and pollution assessment of heavy metals in urban soils of Karachi, Pakistan. \u003cem\u003eEcological Indicators\u003c/em\u003e, 48, 358-364. doi: 10.1016/j.ecolind.2014.08.032.\u003c/li\u003e\n\u003cli\u003eKhan, A., Javid, S., Muhmood, A., Mjeed, T., Niaz, A., \u0026amp; Majeed, A. (2013). Heavy metal status of soil and vegetables grown on peri-urban area of Lahore district. \u003cem\u003eSoil and Environment\u003c/em\u003e, 32(1), 49-54.\u003c/li\u003e\n\u003cli\u003eKhan, M. M., Islam, E., Irem, S., Akhtar, K., Ashraf, M. Y., Iqbal, J., \u0026amp; Liu, D. (2018). Pb-induced phytotoxicity in para grass (\u003cem\u003eBrachiaria mutica\u003c/em\u003e) and Castorbean (\u003cem\u003eRicinus communis\u003c/em\u003e L.): Antioxidant and ultrastructural studies. \u003cem\u003eChemosphere\u003c/em\u003e, 200, 257-265. doi: 10.1016/j.chemosphere.2018.02.101.\u003c/li\u003e\n\u003cli\u003eLInDh, P., \u0026amp; LeMenkOVA, P. (2022). Soil contamination from heavy metals and persistent organic pollutants (PAH, PCB and HCB) in the coastal area of V\u0026auml;sternorrland, Sweden. \u003cem\u003eGospodarka Surowcami Mineralnymi\u0026ndash;Mineral Resources Management\u003c/em\u003e, 38(2), 147-168. doi: 10.24425/gsm.2022.141662.\u003c/li\u003e\n\u003cli\u003eLotfy, S., \u0026amp; Mostafa, A. (2014). Phytoremediation of contaminated soil with cobalt and chromium. \u003cem\u003eJournal of Geochemical Exploration\u003c/em\u003e, 144, 367-373. doi: 10.1016/j.gexplo.2013.07.003.\u003c/li\u003e\n\u003cli\u003eMa, J., Saleem, M. H., Ali, B., Rasheed, R., Ashraf, M. A., Aziz, H., Ercisli, S., Riaz, S., Elsharkawy, M. M., \u0026amp; Hussain, I. (2022). Impact of foliar application of syringic acid on tomato (\u003cem\u003eSolanum lycopersicum\u003c/em\u003e L.) under heavy metal stress-insights into nutrient uptake, redox homeostasis, oxidative stress, and antioxidant defense. \u003cem\u003eFrontiers in Plant Science\u003c/em\u003e, 13, 950120. doi: 10.3389/fpls.2022.950120.\u003c/li\u003e\n\u003cli\u003eMalar, S., Manikandan, R., Favas, P. J., Sahi, S. V., \u0026amp; Venkatachalam, P. (2014). Effect of lead on phytotoxicity, growth, biochemical alterations and its role on genomic template stability in \u003cem\u003eSesbania grandiflora\u003c/em\u003e: a potential plant for phytoremediation. \u003cem\u003eEcotoxicology and environmental safety\u003c/em\u003e, 108, 249-257.doi: https://doi.org/10.1016/j.ecoenv.2014.05.018.\u003c/li\u003e\n\u003cli\u003eMalik, R. N., Jadoon, W. A., \u0026amp; Husain, S. Z. (2010). Metal contamination of surface soils of industrial city Sialkot, Pakistan: a multivariate and GIS approach. \u003cem\u003eEnvironmental geochemistry and health\u003c/em\u003e, 32, 179-191. doi: 10.1007/s10653-009-9274-1.\u003c/li\u003e\n\u003cli\u003eMuhammad, S., Shah, M. T., \u0026amp; Khan, S. (2011). Health risk assessment of heavy metals and their source apportionment in drinking water of Kohistan region, northern Pakistan. \u003cem\u003eMicrochemical journal\u003c/em\u003e, 98(2), 334-343. doi: 10.1016/j.microc.2011.03.003.\u003c/li\u003e\n\u003cli\u003eM\u0026uuml;hlbachov\u0026aacute;, G. 2011. Soil microbial activities and heavy metal mobility in long-term contaminated soils after addition of EDTA and EDDS. \u003cem\u003eEcological Engineering\u003c/em\u003e. 37: 1064\u0026ndash;1071. doi: 10.1016/j.ecoleng.2010.08.004.\u003c/li\u003e\n\u003cli\u003eNakano, Y., \u0026amp; Asada, K. (1981). Hydrogen peroxide is scavenged by ascorbate-specific peroxidase in spinach chloroplasts. \u003cem\u003ePlant and cell physiology\u003c/em\u003e, 22(5), 867-880. doi: 10. 1093/oxfordjournals. pcp. a076 232.\u003c/li\u003e\n\u003cli\u003eNaveed, S., Oladoye, P. O., \u0026amp; Alli, Y. A. (2023). Toxic heavy metals: A bibliographic review of risk assessment, toxicity, and phytoremediation technology. \u003cem\u003eSustainable Chemistry for the Environment\u003c/em\u003e, 100018. doi: 10.1016 /j.scenv. 2023.100018.\u003c/li\u003e\n\u003cli\u003eOlsen, S. R. (1954). Estimation of available phosphorus in soils by extraction with sodium bicarbonate. US Department of Agriculture. \u003c/li\u003e\n\u003cli\u003ePriya, A. K., Muruganandam, M., Ali, S. S., \u0026amp; Kornaros, M. (2023). Clean-Up of Heavy Metals from Contaminated Soil by Phytoremediation: A Multidisciplinary and Eco-Friendly Approach. \u003cem\u003eToxics\u003c/em\u003e, 11(5), 422. doi: 10.3390/toxics11050422.\u003c/li\u003e\n\u003cli\u003eP\u0026uuml;tter, J. (1974). Peroxidases. In \u003cem\u003eMethods of enzymatic analysis\u003c/em\u003e (pp. 685-690). Academic Press.\u003c/li\u003e\n\u003cli\u003eQureshi, F. F., Ashraf, M. A., Rasheed, R., Ali, S., Hussain, I., Ahmed, A., \u0026amp; Iqbal, M. (2020). Organic chelates decrease phytotoxic effects and enhance chromium uptake by regulating chromium-speciation in castor bean (\u003cem\u003eRicinus communis\u003c/em\u003e L.). \u003cem\u003eScience of the Total Environment\u003c/em\u003e, 716, 137061. doi: 10.1016 /j.scitotenv. 2020.137061.\u003c/li\u003e\n\u003cli\u003eRiazi, A., Matsuda, K., \u0026amp; Arslan, A. (1985). Water-stress induced changes in concentrations of proline and other solutes in growing regions of young barley leaves. \u003cem\u003eJournal of Experimental Botany\u003c/em\u003e, 36(11), 1716-1725. doi: 10.1111/j.1399-3054.1992.tb08764.x.\u003c/li\u003e\n\u003cli\u003eSaleem, M. H., Ali, S., Kamran, M., Iqbal, N., Azeem, M., Tariq Javed, M., Ali, Q., Zulqurnain Haider, M., Irshad, S., \u0026amp; Rizwan, M. (2020). Ethylenediaminetetraacetic acid (EDTA) mitigates the toxic effect of excessive copper concentrations on growth, gaseous exchange and chloroplast ultrastructure of \u003cem\u003eCorchorus capsularis\u003c/em\u003e L. and improves copper accumulation capabilities. \u003cem\u003ePlants\u003c/em\u003e, 9(6), 756. doi: 10.3390/plants9060756.\u003c/li\u003e\n\u003cli\u003eSidhu, G. P. S., Singh, H. P., Batish, D. R., \u0026amp; Kohli, R. K. (2016). Effect of lead on oxidative status, antioxidative response and metal accumulation in \u003cem\u003eCoronopus didymus\u003c/em\u003e. \u003cem\u003ePlant physiology and biochemistry\u003c/em\u003e, 105, 290-296. doi: 10.1016/j.plaphy.2016.05.019.\u003c/li\u003e\n\u003cli\u003eSong, X., Zhou, G., Shi, L., Ahmad, I., Shi, X., Zhu, G., \u0026amp; Jiao, X. (2021). Comparative effects of salinity and drought on seed germination, seedling growth, photosynthetic productivity, pigments content and antioxidant enzymes of castor bean (\u003cem\u003eRicinus communis\u003c/em\u003e). \u003cem\u003eCrop and Pasture Science\u003c/em\u003e, 72(7), 541-550. doi: 10.1071/CP20495.\u003c/li\u003e\n\u003cli\u003eSteel, R. G. D., Torrie, J. H., and Dicky, D. A. (1997). Principles and Procedures of Statistics\u0026mdash;A Biometrical Approach, 3rd Edn. New York, NY: McGraw-Hill.\u003c/li\u003e\n\u003cli\u003eTeulat, B., Zoumarou-Wallis, N., Rotter, B., Ben Salem, M., Bahri, H., and This, D. (2003). QTL for relative water content in field-grown barley and their stability across Mediterranean environments. \u003cem\u003eTheoretical and Applied Genetics\u003c/em\u003e.108, 181\u0026ndash;188. doi: 10.1007/s00122-003-1417-7\u003c/li\u003e\n\u003cli\u003eUllah, R., Bakht, J., Shafi, M., Iqbal, M., Khan, A., \u0026amp; Saeed, M. (2011). Phyto-accumulation of heavy metals by sunflower (\u003cem\u003eHelianthus annuus\u003c/em\u003e L.) grown on contaminated soil. \u003cem\u003eAfrican Journal of Biotechnology\u003c/em\u003e, 10(75), 17192-17198. doi: https://doi.org/10.5897/AJB11.1832.\u003c/li\u003e\n\u003cli\u003eUllah, S., Ali, R., Mahmood, S., Atif Riaz, M., \u0026amp; Akhtar, K. (2020). Differential growth and metal accumulation response of \u003cem\u003eBrachiaria mutica\u003c/em\u003e and \u003cem\u003eLeptochloa fusca\u003c/em\u003e on cadmium and lead contaminated soil. \u003cem\u003eSoil and Sediment Contamination: An International Journal\u003c/em\u003e, 29(8), 844-859. doi: 10.1080/15320383.2020.1777935.\u003c/li\u003e\n\u003cli\u003eUllah, S., Mahmood, S., Ali, R., Khan, M. R., Akhtar, K., \u0026amp; Depar, N. (2021). Comparing chromium phyto-assessment in \u003cem\u003eBrachiaria mutica\u003c/em\u003e and \u003cem\u003eLeptochloa fusca\u003c/em\u003e growing on chromium polluted soil. \u003cem\u003eChemosphere\u003c/em\u003e, 269, 128728. doi: 10.1016/j.chemosphere.2020.128728.\u003c/li\u003e\n\u003cli\u003eUllah, S., Mahmood, T., Iqbal, Z., Naeem, A., Ali, R., \u0026amp; Mahmood, S. (2019). Phytoremediative potential of salt-tolerant grass species for cadmium and lead under contaminated nutrient solution. \u003cem\u003eInternational journal of phytoremediation\u003c/em\u003e, 21(10), 1012-1018. doi: 10.1080/15226514.2019.1594683.\u003c/li\u003e\n\u003cli\u003eWalkley, A., \u0026amp; Black, I. A. (1934). An examination of the Degtjareff method for determining soil organic matter, and a proposed modification of the chromic acid titration method. \u003cem\u003eSoil science\u003c/em\u003e, 37(1), 29-38.\u003c/li\u003e\n\u003cli\u003eWang, L., Rinklebe, J., Tack, F. M., \u0026amp; Hou, D. (2021). A review of green remediation strategies for heavy metal contaminated soil. \u003cem\u003eSoil Use and Management\u003c/em\u003e, 37(4), 936-963.\u003c/li\u003e\n\u003cli\u003eWani, Z. A., Ahmad, Z., Asgher, M., Bhat, J. A., Sharma, M., Kumar, A.,\u0026amp; Anjum, N. A. (2023). Phytoremediation of Potentially Toxic Elements: Role, Status and Concerns. \u003cem\u003ePlants\u003c/em\u003e, 12(3), 429. doi: 10.3390/plants12030429.\u003c/li\u003e\n\u003cli\u003eYang, G., Rhodes, D., and Joly, R. J. (1996). Effect of high temperature on membrane stability and chlorophyll fluorescence in glycinebetaine-containing maize lines. \u003cem\u003eAustralian Journal of Plant Physiology.\u003c/em\u003e 23, 431\u0026ndash;443. doi: 10.1071/PP9960437.\u003c/li\u003e\n\u003cli\u003eYang, J., Yang, J., \u0026amp; Huang, J. (2017). Role of co-planting and chitosan in phytoextraction of As and heavy metals by \u003cem\u003ePteris vittata\u003c/em\u003e and castor bean\u0026ndash;a field case. \u003cem\u003eEcological engineering\u003c/em\u003e, 109, 35-40. doi: 10.1016/j.ecoleng.2017.09.001.\u003c/li\u003e\n\u003cli\u003eYang, Y., Liang, Y., Han, X., Chiu, T. Y., Ghosh, A., Chen, H., \u0026amp; Tang, M. (2016). The roles of arbuscular mycorrhizal fungi (AMF) in phytoremediation and tree-herb interactions in Pb contaminated soil. \u003cem\u003eScientific Reports\u003c/em\u003e, 6(1), 20469. doi:10.1038/srep20469.\u003c/li\u003e\n\u003cli\u003eZhou, G., Liu, C., Cheng, Y., Ruan, M., Ye, Q., Wang, R., Yao, Z., \u0026amp; Wan, H. (2022). Molecular evolution and functional divergence of stress-responsive Cu/Zn superoxide dismutases in plants. International \u003cem\u003eJournal of Molecular Sciences\u003c/em\u003e, 23(13), 7082. doi: 10.3390/ijms23137082.\u003c/li\u003e\n\u003cli\u003eZulkernain, N. H., Basant, N., Ng, C. C., Kriti, Salari, M., \u0026amp; Mallick, S. (2023). Recovery of precious metals from e-wastes through conventional and phytoremediation treatment methods: a review and prediction. \u003cem\u003eJournal of Material Cycles and Waste Managemet\u003c/em\u003e, 1-27. doi:10.1007/s10163-023-01717-5.\u003c/li\u003e\n\u003c/ol\u003e"}],"fulltextSource":"","fullText":"","funders":[],"hasAdminPriorityOnWorkflow":false,"hasManuscriptDocX":true,"hasOptedInToPreprint":true,"hasPassedJournalQc":"","hasAnyPriority":false,"hideJournal":true,"highlight":"","institution":"","isAcceptedByJournal":false,"isAuthorSuppliedPdf":false,"isDeskRejected":"","isHiddenFromSearch":false,"isInQc":false,"isInWorkflow":false,"isPdf":false,"isPdfUpToDate":true,"isWithdrawnOrRetracted":false,"journal":{"display":true,"email":"
[email protected]","identity":"researchsquare","isNatureJournal":false,"hasQc":true,"allowDirectSubmit":true,"externalIdentity":"","sideBox":"","snPcode":"","submissionUrl":"/submission","title":"Research Square","twitterHandle":"researchsquare","acdcEnabled":true,"dfaEnabled":false,"editorialSystem":"","reportingPortfolio":"","inReviewEnabled":false,"inReviewRevisionsEnabled":true},"keywords":"Castor bean, phytoremediation, lead uptake, antioxidants, water relation","lastPublishedDoi":"10.21203/rs.3.rs-3344644/v1","lastPublishedDoiUrl":"https://doi.org/10.21203/rs.3.rs-3344644/v1","license":{"name":"CC BY 4.0","url":"https://creativecommons.org/licenses/by/4.0/"},"manuscriptAbstract":"\u003cp\u003eIn Pakistan, probably thousands of hectares are contaminated with heavy metals. As castor plant is hyper-accumulator of heavy metals, its cultivation in the area of lead (Pb) contamination can show great potential in terms of remediation of soils. Present study aimed to evaluate the phytoremediation potential of different castor genotypes, NIAB Gold, NIAB Spineless, NIAB-2020, DS-30 and C-3 grown in pots filled with 5 kg soil, spiked with various concentrations of Pb (0, 100, 200, 400, and 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e). Results showed that plant biomass and photosynthetic pigments reduced significantly with increasing Pb concentrations. Activities of superoxide dismutase and peroxidase were decreased significantly whereas catalase and ascorbate peroxidase were increased with increasing Pb levels in all genotypes. At 800 mg Pb kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e soil, the highest catalase and ascorbate peroxidase activities of 12.23 and 64.43 mM/g FW, respectively, were recorded in DS-30 followed by NIAB-2020. The highest total soluble proteins (8.44 mg g\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e) were recorded in DS-30 followed by NIAB-2020 under Pb contamination at 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e soil. Lead uptake increased significantly with increasing levels of Pb and highest uptake in roots were recorded in NIAB-2020 (302 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e) followed by DS-30 (299 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e) under Pb contamination at 800 mg kg\u003csup\u003e\u0026minus;\u0026thinsp;1\u003c/sup\u003e. All genotypes showed metal translocation factor less than 1 under all Pb levels. In conclusion, NIAB-2020 and DS-30 possessed good potential with better Pb accumulation, osmolytes production and antioxidant activities compared to other castor bean genotypes.\u003c/p\u003e","manuscriptTitle":"Differential growth and metal accumulation response of castor bean genotypes on a lead contaminated soil","msid":"","msnumber":"","nonDraftVersions":[{"code":1,"date":"2023-09-25 23:05:25","doi":"10.21203/rs.3.rs-3344644/v1","editorialEvents":[{"type":"communityComments","content":0}],"status":"published","journal":{"display":true,"email":"
[email protected]","identity":"researchsquare","isNatureJournal":false,"hasQc":true,"allowDirectSubmit":true,"externalIdentity":"","sideBox":"","snPcode":"","submissionUrl":"/submission","title":"Research Square","twitterHandle":"researchsquare","acdcEnabled":true,"dfaEnabled":false,"editorialSystem":"","reportingPortfolio":"","inReviewEnabled":false,"inReviewRevisionsEnabled":true}}],"origin":"","ownerIdentity":"6aca2cca-caf0-4c45-9e17-1db398e05521","owner":[],"postedDate":"September 25th, 2023","published":true,"recentEditorialEvents":[],"rejectedJournal":[],"revision":"","amendment":"","status":"posted","subjectAreas":[],"tags":[],"updatedAt":"2023-10-09T14:29:23+00:00","versionOfRecord":[],"versionCreatedAt":"2023-09-25 23:05:25","video":"","vorDoi":"","vorDoiUrl":"","workflowStages":[]},"version":"v1","identity":"rs-3344644","journalConfig":"researchsquare"},"__N_SSP":true},"page":"/article/[identity]/[[...version]]","query":{"redirect":"/article/rs-3344644","identity":"rs-3344644","version":["v1"]},"buildId":"_2-kVJe1T_tPrBINL-cwx","isFallback":false,"isExperimentalCompile":false,"dynamicIds":[84888],"gssp":true,"scriptLoader":[]}
Text is read by the "Ask this paper" AI Q&A widget below.
Extraction quality varies by source — PMC NXML preserves structure
cleanly, OA-HTML may include some navigation residue, and OA-PDF can
have broken hyphenation. The publisher copy
(via DOI)
is the canonical version.