陕西关中土壤富硒标准研究与探讨——以小麦为例
Exploring selenium enrichment criteria for soils in the Guanzhong area, Shaanxi Province: A case study of wheat
责任编辑: 蒋实
收稿日期: 2022-09-6 修回日期: 2023-03-30
基金资助: |
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Received: 2022-09-6 Revised: 2023-03-30
作者简介 About authors
任蕊(1984-),女,高级工程师,主要从事农业地质调查与地球化学研究工作。Email:
建立陕西省富硒小麦产地土壤硒阈值不仅关系到天然富硒小麦精益化、精细化、精确化生产,更能够提高富硒土地利用效率,促进陕西富硒产业发展。本文以1∶25万土地质量地球化学调查数据为基础,依托陕西省近年来采集的544组土壤及其对应的小麦籽实样品硒含量数据,基于关中地区表层土壤硒地球化学异常下限和小麦—土壤隶属函数结果,提出以0.27×10-6作为陕西省富硒小麦产地土壤硒阈值。实证研究发现,采用随机抽样得到的验证集的小麦富硒率达到83.78%,第三方检验的富硒率高达87.14%,以该阈值圈定的土地生产出的小麦能够满足中国营养学会规定的硒推荐摄入量(60 μg/d),土地面积约为1 500 km2(225万亩),比按0.3×10-6圈出的富硒土地增加了640 km2(96万亩)。由此可见,按照农作物种类有针对性地界定富硒土壤界限值,能够较大程度地提高富硒土地利用效率,促进富硒产业发展,为制定陕西省富硒土壤标准提供科学依据。
关键词:
Establishing the selenium threshold for soils in selenium-rich wheat producing areas in Shaanxi Province is closely related to the lean, fine-scale, and accurate production of natural selenium-rich wheat. Moreover, it can improve the utilization efficiency of selenium-rich land, thus promoting the development of selenium-rich industry in this province. This study determined the selenium threshold of soils in selenium-rich wheat producing areas in Shaanxi at 0.27×10-6 based on the 1∶250 000 land quality geochemical survey data, the selenium concentration data of 544 sets of soil samples and corresponding wheat seed samples collected in Shaanxi in recent years, the lower limit of geochemical anomalies of selenium in topsoil in the Guanzhong area, and the wheat-soil function. The empirical study showed that the validation set formed via random sampling yielded a selenium accumulation rate of 83.78%, while the third-party inspection yielded a selenium accumulation rate of 87.14%. The wheat produced from selenium-rich land delineated based on the selenium threshold 0.27×10-6 satisfies the recommended nutrient intake of selenium (60 μg/d) stipulated by the Chinese Nutrition Society. Furthermore, the area of the selenium-rich land is about 1 500 km2 (2 250 000 mu), increasing by 640 km2 (960 000 mu) compared with that of land delineated based on a selenium threshold of 0.3×10-6. Therefore, determining selenium-rich soil threshold by crop species can greatly improve the utilization efficiency of selenium-rich land, thus promoting the development of the selenium-rich industry. This study provides a scientific basis for setting selenium enrichment criteria for soils in Shaanxi Province.
Keywords:
本文引用格式
任蕊, 张志敏, 王晖, 陈继平, 乔新星, 梁东丽.
REN Rui, ZHANG Zhi-Min, WANG Hui, CHEN Ji-Ping, QIAO Xin-Xing, LIANG Dong-Li.
0 引言
硒元素作用于人体生理的特性和富硒土壤的稀缺性,使得天然富硒农产品有着潜在的巨大消费需求和良好的开发前景。富硒土壤能生产出天然富硒农产品,并通过食物链将硒元素安全、有效地转移到人体,保证人体健康。习近平总书记明确指出要利用好硒这一宝贵资源,把它转化为富硒产业。截至2018年底,陕西省1∶25万土地质量地球化学调查实现关中地区全覆盖,调查面积3.95万km2,区内土壤基本呈碱性[16],按照中国地质调查局推荐的碱性富硒土壤标准下限0.3×1
笔者在陕西关中地区1∶25万土地质量地球化学调查表层土壤数据基础上,系统整理了该地区近10年采集的544组小麦籽粒硒含量数据及其根系土硒含量、pH值数据,对如何界定小麦对应的富硒土壤标准进行了探讨。
1 研究区概况与数据来源
1.1 研究区概况
图1
1.2 样品采集与分析测试
1.2.1 样品采集
陕西省1∶25万土地质量地球化学调查采用网格化方式开展土壤测量工作,表层(0~20 cm)土壤样品的采样密度为1个点/km2,每4 km2组合分析一件样品,共获得表层土壤数据10 114个。将上述表层土壤硒元素含量数据作为区域统计研究的基础数据。
按照土壤硒含量不同区间采集土壤和对应小麦的籽粒样品各544组。小麦样品采用梅花点法进行多点采样,然后等量混匀组成1件混合样品,样品质量大于500 g。与农作物样品采集相配套,同时采集相同点位的农作物根系土,样品质量大于1 000 kg。
1.2.2 样品分析及质量控制
样品分析由自然资源部西安矿产资源检测中心承担。植物和土壤样品均分析全硒含量,分析方法为原子荧光光谱法(AFS)。另外,用pH计电极法(ISE)测定土壤样的pH值。测试过程中加入国家一级标准物质进行分析质量控制,准确度和精密度监控样合格率达98%以上。
2 结果与分析
2.1 关中地区表层土壤硒地球化学含量特征
表1 关中地区表层土壤硒含量分级统计
Table 1
计算方法 | 地球化学定义 | 区间划分 | 表层Se含量区间/10-6 |
---|---|---|---|
累积频率法 (n=10 114) | 低值区 | <5% | w(Se)<0.11 |
低背景区 | 5%~<25% | 0.11≤w(Se)<0.14 | |
背景区 | 25%~<75% | 0.14≤w(Se)<0.20 | |
高背景区 | 75%~<85% | 0.20≤w(Se)<0.22 | |
弱异常区 | 85%~<95% | 0.22≤w(Se)<0.28 | |
异常区 | 95%~<98.5% | 0.28≤w(Se)<0.37 | |
强异常区 | ≥98.5% | w(Se)≥0.37 |
根据表1确定85 %累积频率对应的0.22×10-6为关中地区表层土壤硒元素异常下限值,以此作为确定富硒土壤阈值的重要参考依据。
2.2 小麦硒—土壤硒隶属函数模型
2.2.1 单因素方差分析
将调查区采集的544组小麦及根系土壤样品分析数据采用
表2 小麦样品数据分组统计
Table 2
土壤分组 | 1组 | 2组 | 3组 | 4组 | 5组 | 6组 |
---|---|---|---|---|---|---|
根系土硒含量 | 0.1≤w(Se)<0.2 | 0.2≤w(Se)<0.3 | 0.3≤w(Se)<0.4 | 0.4≤w(Se)<0.5 | 0.5≤w(Se)<0.6 | w(Se)>0.6 |
样本量 | 32 | 174 | 139 | 78 | 46 | 66 |
根系土硒均值 | 0.156 | 0.249 | 0.346 | 0.441 | 0.537 | 0.808 |
小麦硒均值 | 0.079 | 0.086 | 0.133 | 0.207 | 0.255 | 0.488 |
小麦硒最小值 | 0.018 | 0.011 | 0.011 | 0.027 | 0.050 | 0.059 |
小麦硒最大值 | 0.339 | 0.590 | 0.525 | 0.472 | 0.856 | 1.395 |
为了说明土壤硒含量对小麦硒含量有显著影响,采用单因素方差分析法证明不同土壤组别的小麦硒含量间存在显著差异。首先使用方差齐性检验,检验p值为0,小于显著性水平0.05,说明方差不齐。
在方差不齐的情况下,采用Games-Howell检验不同组间的统计差异,由于自变量(根系土硒含量)分为6组,因此因变量小麦硒含量均值共有15种不同的组间组合。除小麦组1和组2,组4和组5的检验p值大于显著性水平0.05,其余13种组合的检验p值均小于显著性水平0.05,说明其余13种组合间的均值差异显著,检验结果见表3。
表3 小麦硒含量的多重比较检验
Table 3
根系土硒 含量组别 | 小麦硒含 量组别 | 显著性 | 根系土硒 含量组别 | 小麦硒含 量组别 | 显著性 | |
---|---|---|---|---|---|---|
1 | 2 | 0.996 | 4 | 1 | 0 | |
3 | 0.009 | 2 | 0 | |||
4 | 0 | 3 | 0 | |||
5 | 0 | 5 | 0.461 | |||
6 | 0 | 6 | 0 | |||
2 | 1 | 0.996 | 5 | 1 | 0 | |
3 | 0 | 2 | 0 | |||
4 | 0 | 3 | 0 | |||
5 | 0 | 4 | 0.461 | |||
6 | 0 | 6 | 0 | |||
3 | 1 | 0.009 | 6 | 1 | 0 | |
2 | 0 | 2 | 0 | |||
4 | 0 | 3 | 0 | |||
5 | 0 | 4 | 0 | |||
6 | 0 | 5 | 0 |
此外,由不同土壤中小麦硒含量均值折线图(图2)也可以看出,除组1和组2、组4和组5之间的均值差异不显著外,其余组两两之间的均值差异均较大。由单因素方差分析检验可知至少一组与其他一组存在显著性差异,则可认为关中地区土壤硒含量对小麦中硒含量有显著影响。
图2
图2
不同土壤中小麦硒含量均值折线
Fig.2
Broken line graph of wheat selenium content in different soils
2.2.2 土壤—小麦硒含量相关性分析
应用双变量相关分析检验指标间的相关性,结果显示:土壤硒含量和小麦中硒含量的相关系数为0.750,所以,关中地区的小麦籽粒中的硒含量与土壤中的硒含量呈现出显著的线性相关性。
2.2.3 土壤硒临界值的确定
对535组小麦及根系土壤样品硒数据,使用随机抽样程序,随机选取59组样本作为验证集,应用476组样本数据建立回归模型。由前述相关分析可知,小麦中的硒含量与土壤中的硒含量呈现出显著的线性相关性,因此对其建立一元线性回归模型,回归方程如下:
其中:X表示土壤硒含量;Y表示小麦硒含量。
检验可决系数
图3
根据此回归方程,当Y(小麦籽粒硒含量)为0.10×10-6时,可确定对应X(土壤硒含量)为0.27×10-6。
2.3 富硒土壤分级指标的确定
根据富硒小麦标准下限值0.10×10-6,计算出对应的土壤硒含量0.27×10-6,高出关中表层土壤硒元素地球化学异常下限值0.22×10-6,确定小麦产地富硒土壤的下限值为0.27×10-6。
由于我国在《食品安全国家标准 食品中污染物限量》(GB 2762—2012)中取消了食品中硒的限量规定,因此,不设小麦产地富硒土壤的上限值。
2018年,我国推出了《土壤环境质量农用地土壤污染风险管控标准(试行)》(GB 15618—2018),旨在对农用地进行分类管理,以保障农产品质量安全。鉴于此,小麦产地富硒土壤标准还对土壤中镉、汞、砷、铅、铬、铜、镍和锌共8种元素含量作了要求,见表4。
表4 陕西小麦产地富硒土壤分级指标
Table 4
指标要求 | 土壤硒含量/ 10-6 | 土壤环境质量 |
---|---|---|
富硒 | w(Se)≥0.27 | 镉、汞、砷、铅、铬、铜、镍和锌元素含量低于GB 15618—2018标准中农用地土壤污染风险筛选值 |
2.4 实证研究
2.4.1 验证集检验
在建立回归模型之前,先使用随机抽样程序,随机选取59组样本作为验证集(样本分布位置见图4),对模型的富硒率进行检验,其中根系土壤硒含量大于(等于)临界值0.27×10-6的37件小麦样品中,31件小麦样品硒含量高于富硒标准下限值0.10×10-6,小麦富硒率达83.78 %。
图4
2.4.2 第三方检验
表5 小麦样品数据统计表(n=76)
Table 5
统计量 | 小麦籽粒硒/ 10-6 | 根系土硒/ 10-6 | 土壤pH |
---|---|---|---|
最小值 | 0.014 | 0.102 | 7.670 |
最大值 | 0.165 | 1.674 | 8.670 |
中位数 | 0.053 | 0.754 | 8.185 |
平均值 | 0.056 | 0.781 | 8.163 |
标准差 | 0.031 | 0.390 | 0.214 |
3 讨论
实际应用方面,根据中国居民膳食指南[30],我国居民每人每日应摄入的谷物在250~400 g,谷物硒约占日均硒摄入量的1/4,按照陕西省富硒小麦标准下限值0.10×10-6,对应的居民日均硒摄入量在100~160 μg/d,满足中国营养学会规定的推荐摄入量(60 μg/d)。因此本次富硒土壤划定工作选用0.10×10-6作为富硒小麦的下限值。
4 结论
农产品市场是开放型完全竞争市场,农产品产量大、可替代性高,因同类农产品上市时间无法拉开距离,因此其市场风险可想而知。富硒农产品自身具有无可替代的属性,加之市场需求逐渐走高,与普通农产品差异较大,因此其市场供求风险相对较小,且有着较大的市场需求空间。同时,伴随着中国老龄化社会的不断发展,人民生活水平的不断提高,健康养生产品更加受到青睐,日益增长的市场需求为富硒农业发展奠定了坚实的基础。
根据本文提出的富硒小麦产地土壤硒含量阈值0.27×10-6,结合《土壤环境质量 农用地土壤污染风险管控标准(试行)》(GB 15618—2018)中规定的风险筛选值,在关中地区共圈定富硒土地1 500 km2(225万亩),该面积比之按0.3×10-6圈出的富硒土地增加了640 km2(96万亩)。由此可见,按照农作物种类有针对性地界定富硒土壤界限值,能够较大程度地提高富硒土地利用效率,促进富硒产业发展。
依据陕西省富硒农作物种植示范基地实测数据[31]:普通面粉价格2.5元/斤,富硒面粉参考价格4.5元/斤,增收2元/斤。以亩产800斤、出粉率60%、种植成本增加160元/亩计算,每亩预计增收2×800×0.6-160=800元。在圈定的富硒小麦产地上种植1万亩小麦,将比普通小麦增收约800万元,因此,该标准如果推广到全省,并形成市场认可的陕西富硒小麦品牌,获得的产值将大幅度地增加陕西农业和农民收入,助力健康陕西行动和乡村振兴战略。
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[J].Previous studies have demonstrated increased serum copper and iron levels and decreased selenium and zinc levels in patients with myocardial infarction. Furthermore, the prognostic value of the levels of trace elements in myocardial infarction has been stressed. We examined serum levels of Cu, Fe, Zn and Se, as well as glutathione peroxidase (GPx), a selenoenzyme with antioxidant properties, and C-reactive protein (CRP), a marker of inflammation, in acute coronary syndromes (ACS) regarding their relationship to cardiac troponins and creatine kinase-MB mass (CK-MBm), important prognostic markers. Serum trace elements, GPx activity and CRP were determined in 70 patients with ACS who were admitted within 12 h after the onset. Differences in these parameters were evaluated in three groups of patients divided according to the levels of cardiac markers: group III consisted of patients with high increases in cTnT, cTnI and CK-MBm (> or =0.9 ng/mL, > or =1.0 ng/mL, > or =30 ng/mL, respectively), patients with milder increases in these markers were included in groups II and I consisted of patients with values just above the upper reference limits. Serum Fe levels increased significantly in group II and even more prominently in group III compared to group I (p = 0.04, 0.002, respectively). There was no significant difference between groups II and III. The increase in serum Cu was significant in group III compared to both groups II and I (p = 0.04, 0.001, respectively). There was no significant difference between groups I and II regarding Cu and Zn. The decrease in serum Se and GPx levels was significant only between groups III and I (p = 0.004 for Se and p = 0.0001 for GPx). CRP levels showed a significant increase in group III compared to groups II and I (p = 0.03 and 0.001). CRP showed a significant positive and GPx a significant negative correlation to the cardiac markers cTnT, cTnI and CK-MBm. Cu was positively correlated to all cardiac markers, while the positive correlation between Fe and cardiac markers was significant only for cTnI. Both Zn and Se were negatively correlated to cTnT, and Se was also to cTnI. In conclusion, the increase in serum levels of Cu and Fe and the decrease in serum levels of Zn and Se in patients with higher levels of troponins and CK-MBm imply that trace element levels are related to the degree of myocardial damage and thus may play a role in the pathogenesis of ischemic heart disease. The strong correlations between cardiac markers and both CRP and GPx suggest that these parameters are promising prognostic factors in acute coronary syndromes.
Selenium in global food system
[J].Food systems need to produce enough of the essential trace element Se to provide regular adult intakes of at least 40 microg/d to support the maximal expression of the Se enzymes, and perhaps as much as 300 microg/d to reduce risks of cancer. Deprivation of Se is associated with impairments in antioxidant protection, redox regulation and energy production as consequences of suboptimal expression of one or more of the Se-containing enzymes. These impairments may not cause deficiency signs in the classical sense, but instead contribute to health problems caused by physiological and environmental oxidative stresses and infections. At the same time, supranutritional intakes of Se, i.e. intakes greater than those required for selenocysteine enzyme expression, appear to reduce cancer risk. The lower, nutritional, level is greater than the typical intakes of many people in several parts of the world, and few populations have intakes approaching the latter, supranutritional, level. Accordingly, low Se status is likely to contribute to morbidity and mortality due to infectious as well as chronic diseases, and increasing Se intakes in all parts of the world can be expected to reduce cancer rates.
Strategies for increasing the selenium content of wheat
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Biofortification of UK food crops with selenium
[J].
DOI:10.1079/pns2006490
PMID:16672078
[本文引用: 1]
Se is an essential element for animals. In man low dietary Se intakes are associated with health disorders including oxidative stress-related conditions, reduced fertility and immune functions and an increased risk of cancers. Although the reference nutrient intakes for adult females and males in the UK are 60 and 75 microg Se/d respectively, dietary Se intakes in the UK have declined from >60 microg Se/d in the 1970s to 35 microg Se/d in the 1990s, with a concomitant decline in human Se status. This decline in Se intake and status has been attributed primarily to the replacement of milling wheat having high levels of grain Se and grown on high-Se soils in North America with UK-sourced wheat having low levels of grain Se and grown on low-Se soils. An immediate solution to low dietary Se intake and status is to enrich UK-grown food crops using Se fertilisers (agronomic biofortification). Such a strategy has been adopted with success in Finland. It may also be possible to enrich food crops in the longer term by selecting or breeding crop varieties with enhanced Se-accumulation characteristics (genetic biofortification). The present paper will review the potential for biofortification of UK food crops with Se.
Selenium in food and the human body:A review
[J].DOI:10.1016/j.scitotenv.2008.06.024 URL [本文引用: 1]
Selenium fertilization strategies for bio-fortification of food:An agro-ecosystem approach
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Relationships between the selenium content in flue-cured tobacco leaves and the selenium content in soil in Enshi,China tobacco-growing area
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Selenium deficiency risk predicted to increase under future climate change
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Selenium:Environmental significance,pollution,and biological treatment technologies
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Selenium distribution in the chinese environment and its relationship with human health:A review
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The epidemiology of selenium deficiency in the etiology of endemic diseases in China
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陕西关中地区土壤硒分布特征及影响因素
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Distribution of soil selenium in Guanzhong Area and its influencing factors
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Selenium in higher plants
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Mechanisms of selenium enrichment and measurement in brassicaceous vegetables and their application to human health
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DOI:10.3389/fpls.2017.01365
PMID:28824693
[本文引用: 1]
Selenium (Se) is an essential micronutrient for human health. Se deficiency affects hundreds of millions of people worldwide, particularly in developing countries, and there is increasing awareness that suboptimal supply of Se can also negatively affect human health. Selenium enters the diet primarily through the ingestion of plant and animal products. Although, plants are not dependent on Se they take it up from the soil through the sulphur (S) uptake and assimilation pathways. Therefore, geographic differences in the availability of soil Se and agricultural practices have a profound influence on the Se content of many foods, and there are increasing efforts to biofortify crop plants with Se. Plants from the Brassicales are of particular interest as they accumulate and synthesize Se into forms with additional health benefits, such as methylselenocysteine (MeSeCys). The Brassicaceae are also well-known to produce the glucosinolates; S-containing compounds with demonstrated human health value. Furthermore, the recent discovery of the selenoglucosinolates in the Brassicaceae raises questions regarding their potential bioefficacy. In this review we focus on Se uptake and metabolism in the Brassicaceae in the context of human health, particularly cancer prevention and immunity. We investigate the close relationship between Se and S metabolism in this plant family, with particular emphasis on the selenoglucosinolates, and consider the methodologies available for identifying and quantifying further novel Se-containing compounds in plants. Finally, we summarize the research of multiple groups investigating biofortification of the Brassicaceae and discuss which approaches might be most successful for supplying Se deficient populations in the future.
Analysis of selenium accumulation,speciation and tolerance of potential selenium hyperaccumulator Symphyotrichum ericoides
[J].
DOI:10.1111/ppl.12149
PMID:24423113
[本文引用: 1]
Symphyotrichum ericoides was shown earlier to contain hyperaccumulator levels of selenium (Se) in the field (>1000 mg kg(-1) dry weight (DW)), but only when growing next to other Se hyperaccumulators. It was also twofold larger next to hyperaccumulators and suffered less herbivory. This raised two questions: whether S. ericoides is capable of hyperaccumulation without neighbor assistance, and whether its Se-derived benefit is merely ecological or also physiological. Here, in a comparative greenhouse study, Se accumulation and tolerance of S. ericoides were analyzed in parallel with hyperaccumulator Astragalus bisulcatus, Se accumulator Brassica juncea and related Asteraceae Machaeranthera tanacetifolia. Symphyotrichum ericoides and M. tanacetifolia accumulated Se up to 3000 and 1500 mg Se kg(-1) DW, respectively. They were completely tolerant to these Se levels and even grew 1.5- to 2.5-fold larger with Se. Symphyotrichum ericoides showed very high leaf Se/sulfur (S) and shoot/root Se concentration ratios, similar to A. bisulcatus and higher than M. tanacetifolia and B. juncea. Se X-ray absorption near-edge structure spectroscopy showed that S. ericoides accumulated Se predominantly (86%) as C-Se-C compounds indistinguishable from methyl-selenocysteine, which may explain its Se tolerance. Machaeranthera tanacetifolia accumulated 55% of its Se as C-Se-C compounds; the remainder was inorganic Se. Thus, in this greenhouse study S. ericoides displayed all of the characteristics of a hyperaccumulator. The larger size of S. ericoides when growing next to hyperaccumulators may be explained by a physiological benefit, in addition to the ecological benefit demonstrated earlier. © 2014 Scandinavian Plant Physiology Society.
Shaanxi statistical yearbook-2021
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安徽省富硒土壤评价标准及富硒土壤成因浅析
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Evaluation standards and genesis of selenium-rich soil in Anhui Province
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Assessment of bioavailability of selenium in different plant-soil systems by diffusive gradients in thin-films (DGT)
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DOI:S0269-7491(16)31446-4
PMID:28341328
[本文引用: 1]
Uptake of selenium (Se) by plants largely depend on the availability of Se in soil. Soils and plants were sampled four times within 8 weeks of plant growth in pot experiments using four plant species. Sequential extraction and diffusive gradients in thin-films (DGT) method were employed to measure Se concentrations in potted soils in selenite- or selenate-amended soils. Results showed that DGT-measured Se concentrations (C-Se) were generally several folds higher for selenate than selenite amended soils, which were obviously affected by the plant species and the duration of their growth. For example, the folds in soil planted with mustard were 1.49-3.47 and those in soils planted with purple cabbage and broccoli, which grew for 3 and 4 weeks after sowing, were 1.06-2.14 and only 0.15-0.62 after 6 weeks of growth. The selenate-amended soil planted with wheat showed an extremely high C-Se compared with selenite-amended soil, except the last harvest. Furthermore, minimal changes in C-Se and soluble Se(IV) were found in selenite-amended soils during plant growth, whereas significant changes were observed in selenate-amended soils (p < 0.05). Additionally, Se distribution in various fractions of soil remarkably changed; the soils planted with purple cabbage and broccoli showed the most obvious change followed by wheat and mustard. Soluble Se(VI) and exchangeable Se(VI) were likely the major sources of C-Se in selenate-amended soils, and soluble Se(IV) was the possible source of C-Se in selenite-amended soils. In selenate-amended soils, soluble Se(VI) and exchangeable Se(VI) were significantly correlated with Se concentrations in purple cabbage, broccoli, and mustard; in wheat, Se concentration was significantly correlated only with soluble Se(VI) but not with exchangeable Se. C-Se eventually became positively correlated with Se concentrations accumulated by different plants, indicating that DGT is a feasible method in predicting plant uptake of selenate but not of selenite.Copyright © 2017 Elsevier Ltd. All rights reserved.
Environmental selenium research:From microscopic processes to global under-standing
[J].DOI:10.1021/es203434d URL [本文引用: 1]
Selenium cycling across soil-plant-atmosphere interfaces:A critical review
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DOI:10.3390/nu7064199
PMID:26035246
[本文引用: 1]
Selenium (Se) is an essential element for humans and animals, which occurs ubiquitously in the environment. It is present in trace amounts in both organic and inorganic forms in marine and freshwater systems, soils, biomass and in the atmosphere. Low Se levels in certain terrestrial environments have resulted in Se deficiency in humans, while elevated Se levels in waters and soils can be toxic and result in the death of aquatic wildlife and other animals. Human dietary Se intake is largely governed by Se concentrations in plants, which are controlled by root uptake of Se as a function of soil Se concentrations, speciation and bioavailability. In addition, plants and microorganisms can biomethylate Se, which can result in a loss of Se to the atmosphere. The mobilization of Se across soil-plant-atmosphere interfaces is thus of crucial importance for human Se status. This review gives an overview of current knowledge on Se cycling with a specific focus on soil-plant-atmosphere interfaces. Sources, speciation and mobility of Se in soils and plants will be discussed as well as Se hyperaccumulation by plants, biofortification and biomethylation. Future research on Se cycling in the environment is essential to minimize the adverse health effects associated with unsafe environmental Se levels.
中国居民膳食指南科学研究报告(2021)
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Scientific research report on dietary guidelines for chinese residents(2021)
[R].
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