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Home-Journal Online-2017 No.3

Influences of soil cadmium content on bind and fruit cadmium contentsin watermelon

Online:2018/1/15 16:27:17 Browsing times:
Author: LI Han, WANG Zhiwei, SUN Bo, ZOU Tian, SUN Xiaowu
Keywords: Watermelon; Bind; Fruit; Soil; Cadmium
DOI: 10.13925/j.cnki.gsxb.20160307
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PDF Abstract

Abstract:ObjectiveWatermelons are Cucurbitaceae plants, which are juicy and sweet, refreshing andloved by people everywhere. It is a fruit for summer consumption. The Hunan region has a long history ofwatermelon cultivation, with its wide open areas, an annual planting space of about 140 000 hectares, whichranks fourth in the country, providing considerable economic benefit, and it also represents an importanthorticultural crop for the Hunan region. The increased development of the economy and society, the exploitation of minerals, smelting, transportation and the use of mineral fertilizers, has caused cadmium (Cd) to become one of the main pollutants in the environment. The most effective way to control Cd contaminated soilis to cultivate and grow crop varieties with a low accumulation of non-edible plants and edible organs.They will not only provide for the gradual elimination of cadmium in the soil, but also provide for the rational use of the land, and to ensure sustainable land output. Within the Hunan province, heavy metal exceedsthe standards as part of the adjustment of the planting structure, while also having a mild and moderate areathat makes it ideal for watermelon planting. However, cadmium exceeded the standard allowed in the production of the watermelon fruit, with the cadmium content in excess of the standard, and therefore, thethreshold value of the cadmium content of the soil and the cadmium content of the watermelon fruit is a significant issue of concern, and also represents an important reference for the planting structure adjustment.MethodsBy using the potted soil method, and respectively digging soil with different levels of cadmiumpollution in Zhuzhou County of Hunan Province as follows: T1 (Cd: 1.9 mg·kg- 1, pH 5.6); T2 (Cd: 3.59mg·kg-1, pH 5.34); T3 (Cd: 7.03 mg·kg-1, pH 5.48), detection of the Cd contentsoil physical and chemicalindicator of the soil in the laboratory, and digging the soil from the experimental field of the College of horticulture and landscape architecture, Hunan Agricultural University (Cd: 0.21 mg·kg-1, pH 5.12) for comparison, we obtained a pot that is 44 cm wide, 48 cm long, 26 cm high. On April 10th, the following was implemented: 2 leaves and 1 heart of the watermelon seedlings were planted in a pot with 1 plant per pot, usingsingle vine pruning, with each plant having 1 melon. Our approach is to grow 5 pots per treatment, and repeat 3 times. Three of the watermelon plants which were consistent with the growth of the fruit were selectedfor further testing. The cadmium content of the roots, lower stem leaves (fruit section under section 4 tobase), middle stem leaves (4 section around the fruit), upper stem leaves (4 section from fruit to stem tip)and the fruit of watermelon were analyzed.ResultsThe results show that the Cd content in the roots of allthe cultivars increased with the increase of Cd concentration in the soil, T3 > T2 > T1 > CK, The root Cdcontent in theHeimawangziwas 2.64 times, 5.63 times and 6.02 times higher than that in the control. Inthe Cd content in the rootHeimeiniang, each treatment was 3.56 times, 4.56 times and 5.66 times higherthan in the control. The cadmium content in all treatments of theHeimawangzilower stem leaves increased by 2.04 times, 6.22 times and 10.80 times compared to the control; the cadmium content in thetreatments of theHeimeiniangof the lower stem leaves were increased by 3.37 times, 4.79 times and10.3 times compared to the contro; 25.46 mg·kg-1 was the highest Cd content in the lower part of theHeimawangziin the T3 soil. The accumulation amount of Cd in the middle leaves was significantly lower thanthat in the lower part. TheHeimawangzicentral stem and leaf cadmium content increased 137.57% ,432.56%and 611.18%, and the Heimeiniangfor each treatment increased 227.2%, 380.31%and 756.95%compared to the control. The upper stems and leaves represent the tender newborn portions of the plants,and the accumulation of cadmium is relatively small. The contents of Cd in the upper leaves of the watermelons were significantly different in the various soil treatments. TheHeimawangziof the upper leaves increased by 152.93%, 399.98% and 563.05% and theHeimeiniangincreased 170.54%, 418.82% and619.55% compared to the control. The Cd content in the watermelon fruit was positively correlated with theCd content in the soil, and increased with the increase of the Cd content in the soil. The cadmium contentof the watermelon fruits was lower than that of the national standard. T3 with high cadmium content in theHeimawangzireached 0.036 mg·kg-1, 0.011 mg·kg-1 higher than in theHeimeiniang. The enrichmentcoefficient of Cd in the watermelon fruit was much lower than that in the root and stem. The Cd was primarily accumulated in the lower part of the stem and leaf, while the control was enriched in the root. The transfer coefficient of cadmium in different parts of the watermelon increased with the increase of the cadmiumcontent in the soil.ConclusionAccording to the fitting equation of the cadmium content in the soil andfruit of the different cadmium contents during the fruit ripening stagewe observed that the fruit cadmiumcontent reached the national standard allowable value 0.05 mg·kg-1, and the soil cadmium contentHeimawangziandHeimeiniangcorresponded to the 10.04 mg·kg-1, and 12.69 mg·kg-1 values.