Secondary ion mass spectrometry (SIMS) is a sensitive, high resolution technique capable of determining the location of elements or ions in a sample down to sub-cellular levels. The distribution of elements or ions are superimposed onto an image of the plant cell or tissue generated by ion-induced secondary electrons, allowing a visual representation of their positions in the sample. The elements are separated by their mass/charge ratios which can lead to a loss of sensitivity when separating signals from elements with very similar masses such as 16O2 (31·990 a.m.u.) and32 S (31·972 a.m.u.). The abundance of 34S isotope was, therefore enriched, allowing sulphur to be located at the starch granule/protein interface of the mature wheat grain. This demonstrates that isotopic enrichment can be used to extend the applications of SIMS technology to biological systems.
<p indent="0mm">Cadmium (Cd), as a class one carcinogen, is easily transferred from soil to the food chain, representing a potential threat to human health. Rapid industrialization in China during the last three decades has caused widespread contamination in agricultural soils. As a result, a considerable proportion of the rice grain in some areas of southern China has concentrations of Cd exceeding the Chinese food safety standard. This problem has raised a widespread concern regarding food safety and brought a big debate in China about whether the current food safety standard is reasonable. The food safety standard of Cd is not only critical for assessing soil environmental quality, but also important to reduce the current elevated dietary Cd intake for the general population. In this perspective, we summarize the history of establishment and revision in Chinese food safety standards of Cd in staple foods and discuss whether the current Cd safety limits for both rice and wheat are reasonable in terms of the tolerable limit for dietary Cd intake, dietary pattern, the current exposure level of Cd for the general pollution, and social-economic and international trading factors. The dietary Cd intake for the general population has doubled over the last <sc>25 years,</sc> from <sc>13.8 μg/d</sc> in 1990 to <sc>32.7 μg/d</sc> in 2011–2015, with the latter being approximately 61% of the provisional tolerable intake recommended by the Joint FAO/WHO Expert Committee on Food Additives (JECFA). The growing body of evidence suggests no safe Cd intake limit for human health and consequently, dietary intake of Cd should be reduced as much as possible. The milling (i.e., polishing) process has an uncertain effect on change in Cd concentration in polished rice compared to the brown rice because of the uncertainty of the Cd spatial distribution pattern in rice grain. Furthermore, polished rice has higher bioavailability of Cd to humans than brown rice. These differences should be considered when extrapolating the food safety standard between brown rice and polished rice. According to the current exposure level and risk of Cd through consumption of rice, we contend that the current food safety limit for rice grain <sc>(0.2 mg/kg)</sc> in China is lenient for both the southern and northern general populations. It is unadvisable to be looser in further revisions of Chinese food safety standards. For wheat grain, the current safety limit <sc>(0.1 mg/kg)</sc> is reasonable for the northern population but strict for the southern population. Given the current contamination status and national food security and safety, the principle of ALARA (as low as reasonably achievable) should be applied to guild the amendment of the national food safety standard of Cd. There are several scientific perspectives to be further studied. First, epidemiological studies are required to establish the tolerable intake limit suitable to the Chinese ethnic characteristics and dietary patterns. Second, the new food safety standard should consider the subgroup populations with high Cd exposure risk, including infants, children, and local farmers who mainly consume home-grown rice with elevated Cd concentrations in Cd-contaminated regions. To reduce Cd exposure to the local population, effective mitigation strategies include exchanging high Cd home-grown rice with low Cd rice and increasing dietary nutrients and human nutrition.
No abstract is provided for this article.
Phthalate esters (PAEs), widely used as plasticizers in mulching films, are emerging contaminants of concern in farmland soils. However, systematic data on their pollution characteristics and health risks in long-term mulched soils across China remain limited. In this study, 53 typically mulched farmland soil samples from 29 provinces were analyzed using gas chromatography-tandem mass spectrometry to investigate PAEs occurrence, spatial distribution, drivers, and risks. Method validation showed recoveries of 76.3–111.6 % for 16 PAEs, with limits of detection and quantification ranging from 0.2–3.7 ng/mL and 0.1–0.8 ng/mL, respectively. Results revealed Σ16PAE concentrations of 108–2970 μg/kg (mean: 852 μg/kg), with elevated levels in southern/eastern China. Di-isobutyl phthalate and di-butyl phthalate (DBP) showed 100 % detection rates, while DBP dominated contamination (mean: 323 μg/kg). Redundancy analysis identified precipitation and polyethylene microplastic abundance as key drivers. Although non-carcinogenic risks (hazard quotients <1) were low, di(2-ethylhexyl) phthalate posed carcinogenic risks exceeding 10⁻⁴ in 11.3 % of samples. This nationwide assessment highlights the urgency to regulate PAEs emissions from plastic mulch residues and prioritize child health protection in agricultural policies.
No abstract is provided for this article.
• Metal hyperaccumulation has been proposed as a plant defensive strategy. Here, we investigated whether cadmium (Cd) hyperaccumulation protected Thlaspi caerulescens from leaf feeding damage by thrips (Frankliniella occidentalis). • Two ecotypes differing in Cd accumulation, Ganges (high) and Prayon (low), were grown in compost amended with 0–1000 mg Cd kg−1 in two experiments under glasshouse conditions. F2 and F3 plants from the Prayon × Ganges crosses were grown with 5 mg Cd kg−1. Plants were naturally colonized by thrips and the leaf feeding damage index (LFDI) was assessed. • The LFDI decreased significantly with increasing Cd in both ecotypes, and correlated with shoot Cd concentration in a log-linear fashion. Prayon was more attractive to thrips than Ganges, but the ecotypic difference in the LFDI was largely accounted for by the shoot Cd concentration. In the F2 and F3 plants, the LFDI correlated significantly and negatively with shoot Cd, but not with shoot zinc (Zn) or sulphur (S) concentrations. • We conclude that Cd hyperaccumulation deters thrips from feeding on T. caerulescens leaves, which may offer an adaptive benefit to the plant.
No abstract is provided for this article.
No abstract is provided for this article.
In a model hyperaccumulation study a Cd/Zn hyperaccumulator Thlaspi caerulescens accession Ganges and a recently reported Cd/Zn hyperaccumulator Thlaspi praecox grown in increasing Cd and Zn concentrations in the substrate and in field collected polluted soil were compared. Plant biomass, concentrations of Cd and Zn, total chlorophylls and anthocyanins, antioxidative stress parameters and activities of selected antioxidative enzymes were compared. Increasing Cd, but not Zn in the substrate resulted in the increase of biomass of roots and shoots of T. praecox and T. caerulescens. The two species hyperaccumulated Cd in the shoots to a similar extent, whereas T. caerulescens accumulated more Zn in the shoots than T. praecox. Cadmium amendment decreased total chlorophyll concentration and glutathione reductase activity, and increased non-protein thiols concentration only in T. praecox, suggesting that it is less tolerant to Cd than T. caerulescens. In the field-contaminated soil, T. caerulescens accumulated higher Cd concentrations; but as T. praecox produced higher biomass, both species have similar ability to extract Cd.