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《植物生态学报》2015,39(9):932
The concept of ecological thresholds was raised in the 1970s. However, it was subsequently given different definitions and interpretations depending on research fields or disciplines. For most scientists, ecological thresholds refer to the points or zones that link abrupt changes between alternative stable states of an ecosystem. The measurement and quantification of ecological thresholds have great theoretical and practical significance in ecological research for clarifying the structure and function of ecosystems, for planning sustainable development modes, and for delimiting ecological red lines in managing the ecosystems of a region. By reviewing the existing concepts and classifications of ecological thresholds, we propose a new concept and definition at two different levels: the ecological threshold points, i.e. the turning points of quantitative changes to qualitative changes, which can be considered as ecological red lines; the ecological threshold zones, i.e. the regime shifts of the quantitative changes among different stable states, which can be considered as the yellow and/or orange warning boundaries of the gradual ecological changes. The yellow thresholds mean that an ecosystem can return to a stable state by its self-adjustment, the orange thresholds indicate that the ecosystem will stay in the equilibrium state after interference factors being removed, whereas the red thresholds, as the critical threshold points, indicate that the ecosystem will undergo irreversible degradation or even collapse beyond those points. We also summarizes two types of popular Methods in determining ecological thresholds: statistical analysis and modeling based on data of field observations. The applications of ecological thresholds in ecosystem service, biodiversity conservation and ecosystem management research are also reviewed. Future research on ecological thresholds should focus on the following aspects: (1) methodological development for measurement and quantification of ecological thresholds; (2) emphasizing the scaling effect of ecological thresholds and establishment of national-scale observation system and network; and (3) implementation of ecological thresholds as early warning tools in ecosystem management and delimiting ecological red lines. 相似文献
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Summary An in vitro method to simulate pollen development was developed in maize (Zea mays L.). Microspores at the late uninucleate to early binucleate stage were isolated and cultured under various conditions. Cell viability, starch content and the formation of the three nuclei as found in normal mature pollen were monitored during the course of the culture. Media composition was modified in order to promote starch accumulation and frequency of mitosis, while maintaining the viability of the microspores. Under the best conditions, up to 12% of the microspores matured in vitro into trinucleate, starch-filled viable pollen grains which were unable to germinate or produce seeds. At different stages during in vitro maturation, proteins patterns were analyzed and compared with their in vivo equivalent and the patterns were only partially similar. 相似文献
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The hydrology of the Loosdrecht lakes area 总被引:5,自引:5,他引:0
96.
Summary
The gene encoding the porcine growth hormone (GH) has been localized to the q-arm of chromosome 12 using high-resolution R-banded chromosomes for in situ hybridization. We report here the localization of GH on the p-arm of this chromosome when using in situ hybridization on high-resolution G-banded chromosomes. Sequential Q- and R-banding show that this discrepancy is caused by a reversed orientation of chromosome 12 in the R-banded high-resolution karyotype published by Rønne et al. (1987) and the G-banded standard karyotype. 相似文献
The gene encoding the porcine growth hormone (GH) has been localized to the q-arm of chromosome 12 using high-resolution R-banded chromosomes for in situ hybridization. We report here the localization of GH on the p-arm of this chromosome when using in situ hybridization on high-resolution G-banded chromosomes. Sequential Q- and R-banding show that this discrepancy is caused by a reversed orientation of chromosome 12 in the R-banded high-resolution karyotype published by Rønne et al. (1987) and the G-banded standard karyotype. 相似文献
97.
We report the cases of two patients with head and neck Merkel cell carcinoma (MCC) who developed local recurrences confirmed by cytopathology. Interphase fluorescent in situ hybridization (FISH) analysis was performed for research purposes using centromeric probes of chromosomes 6 and 8, on cytological slides. Trisomy of chromosome 6 was found in 85% of tumour cells in the first case of MCC and case 2 exhibited trisomy 8 in 77% of tumour cells. In the absence of specific molecular markers, detection of trisomy 6 and/or trisomy 8 could help in identifying MCC. FISH analysis is easily and quickly performed on interphase nuclei obtained through fine needle aspiration and may be extended to the study of other relevant genetic abnormalities. 相似文献
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We studied long-term (2002–2009) demographics of bobolinks (Dolichonyx oryzivorus) and savannah sparrows (Passerculus sandwichensis) breeding in rotationally grazed systems in the northeastern United States. Both nest success (6–44% bobolink; 7–48% savannah sparrow) and annual productivity (0.43–2.83 bobolink; 0.70–2.35 savannah sparrow) varied annually. Predation (48%) and trampling by cows (32%) accounted for most failed nests. Annual adult apparent survival ranged from 23% to 85% and showed substantial variation by species and sex. Although grazing resulted in substantial loss of vegetative cover, savannah sparrows responded similarly to predation and grazing-induced nest failure (time to renest, distance moved between nests) and generally remained in the same paddock to renest. Minimum paddock size to accommodate one female within this rotation was 70 m × 70 m (0.49 ha), allowing a female to stay within a paddock and move (approx. 50 m) between nesting attempts. To balance pasturing objectives and birds' needs in paddocks first grazed before 25 June, managers in the Northeast should rest that paddock 42–50 days before the second grazing. © 2011 The Wildlife Society. 相似文献
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