The fate of sulfonamides in microenvironments of rape and hot pepper rhizosphere soil system.

Sulfonamides (SAs) in agricultural soils can be degraded in rhizosphere, but can also be taken up by vegetables, which thereby poses human health and ecological risks. A glasshouse experiment was conducted using multi-interlayer rhizoboxes to investigate the fate of three SAs in rape and hot pepper rhizosphere soil systems to examine the relationship between the accumulation and their physicochemical processes. SAs mainly entered pepper shoots in which the accumulation ranged from 0.40 to 30.64 mg kg-1, while SAs were found at high levels in rape roots ranged from 3.01 to 16.62 mg kg-1. The BCFpepper shoot exhibited a strong positive linear relationship with log Dow, while such relationship was not observed between other bioconcentration factors (BCFs) and log Dow. Other than lipophilicity, the dissociation of SAs may also influence the uptake and translocation process. Larger TF and positive correlation with log Dow indicate preferential translocation of pepper SAs. There was a significant (p < 0.05) dissipation gradient of SAs observed away from the vegetable roots. In addition, pepper could uptake more SAs under solo exposure, while rape accumulated more SAs under combined exposure. When SAs applied in mixture, competition between SAs might occur to influence the translocation and dissipation patterns of SAs.

The phloem and xylem structure of plants and the neutral and ionic partitioning of sulfonamides (SAs) influence the uptake and translocation of SAs.A significant (p < 0.05) dissipation gradient of SAs was observed away from the vegetable roots.Combined exposure could promote the correlation between log BCF and log D_ow.

[Research progress on the ecological roles of 'marine ecosystem engineers'.] / "海洋生态系统工程师"åŠå ¶ç”Ÿæ€ä½œç”¨.

'Marine ecosystem engineers' are marine species that can shape habitats and benefit other marine organisms, which are widely found in marine plants, animals and microorganisms. Their ecological roles are the basis of marine ecological functions. By analyzing the relevant literature, we systematically reviewed the research progress of the ecological roles of 'marine ecosystem engineers', and proposed the main research direction and content in the future. In general, 'marine ecosystem engineers' play an active role in a particular marine environment. However, once they become invasive species, they may have negative impacts on the invasive sea area. In addition, some 'marine ecosystem engineers' can have both positive and negative impacts simultaneously. In the future, it is necessary to strengthen researches on the role of 'marine ecosystem engineers' in marine biological beds, marine biogenic reefs, marine biofilms and composite ecosystem engineering, effectively utilize their positive roles and prevent and control their negative impacts, so as to realize the comprehensive development, utilization and protection of the ocean.

Prey Lysate Enhances Growth and Toxin Production in an Isolate of Dinophysis acuminata.

The physiological and toxicological characteristics of Dinophysis acuminata have been increasingly studied in an attempt to better understand and predict diarrhetic shellfish poisoning (DSP) events worldwide. Recent work has identified prey quantity, organic nitrogen, and ammonium as likely contributors to increased Dinophysis growth rates and/or toxicity. Further research is now needed to better understand the interplay between these factors, for example, how inorganic and organic compounds interact with prey and a variety of Dinophysis species and/or strains. In this study, the exudate of ciliate prey and cryptophytes were investigated for an ability to support D. acuminata growth and toxin production in the presence and absence of prey, i.e., during mixotrophic and phototrophic growth respectively. A series of culturing experiments demonstrated that the addition of ciliate lysate led to faster dinoflagellate growth rates (0.25 ± 0.002/d) in predator-prey co-incubations than in treatments containing (1) similar levels of prey but without lysate (0.21 ± 0.003/d), (2) ciliate lysate but no live prey (0.12 ± 0.004/d), or (3) monocultures of D. acuminata without ciliate lysate or live prey (0.01 ± 0.007/d). The addition of ciliate lysate to co-incubations also resulted in maximum toxin quotas and extracellular concentrations of okadaic acid (OA, 0.11 ± 0.01 pg/cell; 1.37 ± 0.10 ng/mL) and dinophysistoxin-1 (DTX1, 0.20 ± 0.02 pg/cell; 1.27 ± 0.10 ng/mL), and significantly greater total DSP toxin concentrations (intracellular + extracellular). Pectenotoxin-2 values, intracellular or extracellular, did not show a clear trend across the treatments. The addition of cryptophyte lysate or whole cells, however, did not support dinoflagellate cell division. Together these data demonstrate that while certain growth was observed when only lysate was added, the benefits to Dinophysis were maximized when ciliate lysate was added with the ciliate inoculum (i.e., during mixotrophic growth). Extrapolating to the field, these culturing studies suggest that the presence of ciliate exudate during co-occurring dinoflagellate-ciliate blooms may indirectly and directly exacerbate D. acuminata abundance and toxigenicity. More research is required, however, to understand what direct or indirect mechanisms control the predator-prey dynamic and what component(s) of ciliate lysate are being utilized by the dinoflagellate or other organisms (e.g., ciliate or bacteria) in the culture if predictive capabilities are to be developed and management strategies created.

[Heavy metal pollution ecology of macro-fungi: research advances and expectation].

Macro-fungi are the main component of biosphere and one of the ecological resources, and play very important roles in matter cycling and in maintaining ecological balances. This paper summarized and reviewed the research advances in the eco-toxicological effects of heavy metals on macro-fungi, the bioaccumulation function of macro-fungi on heavy metals, the ecological adaptation mechanisms of macro-fungi to heavy metal pollution, the role of macro-fungi as a bio-indicator of heavy metal pollution, and the potential of macro-fungi in the ecological remediation of contaminated environment. To strengthen the researches on the heavy metal pollution ecology of macro-fungi would be of practical significance in the reasonable utilization of macro-fungi resources and in the ecological remediation of contaminated environment.

[Bioaccumulation of heavy metals in macrofungi and its application in ecological remediation].

As an important type of environmental biological resources, macrofungi are vitally useful in our life. Compared with green plants, macrofungi can accumulate high concentrations of heavy metals such as Cd, Pb and Hg. In this paper, the bioaccumulation of heavy metals in macrofungi and the advantages of using macrofungi in ecological remediation of heavy metals pollution were discussed. The main factors affecting the bioaccumulation of heavy metals in macrofungi, include the species, ecological types, bioaccumulation characteristics and genetic potentials of macrofungi, the morphologic traits, parts and lifetime of mycelium and fruiting bodies, the intervals between fructifications, and the ecological environments. It was suggested that to screen out the macrofungi with effective bioaccumulation of heavy metals, be prone to artificially cultured, better adjustable to environments and easily post-disposed would be the important domain to be explored in the future.