To investigate the butterfly diversity in Chongqing Municipality, we selected five sampling sections along a gradient of urbanization from Shaping District to Beibei District, namely Shaping Park, Nanxikou, Huitoupo, Jigong Mountain, and Jinyun Mountain. A total of 4,802 butterfly individuals were collected, belonging to 11 families and 41 genera. Of these, the dominant species are Pieris canidia, P. rapae, and Pseudozizeeria maha, while common species are Graphium sarpedon, Eurema hecabe, Lethe syrcis, Polygonia caureum, Tongeia filicaudis, and Parnara guttata. The diversity indexes ranked in the following order:Jinyun Moun-tain>Huitoupo>Jigong Mountain>Nanxikou>Shaping Park. It is concluded that butterfly diversity, which is the highest in Jinyun Mountain and lowest in Shaping Park, increases with vegetation richness, vegetation coverage, and sunlight. Being significantly impacted by urbanization, butterfly diversity can serve as an effective indicator of urban environmental quality and change.
As one of the five major global environmental problems, invasive species have posed serious threats to native ecosystems, public health, and regional economies. Although much progress has been made in the field of biological invasions research in China over the last decade, there are still large knowledge gaps. This paper reviews progress in the field of biological invasions research since 2000 as it relates to China, covering the diversity, colonization and immigration patterns of invasive species, mechanisms and ecological effects of biological invasions, and management and control of invasive species. In China, 529 invasive alien species have been identified, which originated primarily from South and North America, and the major taxa included terrestrial plants, terrestrial invertebrates, and microorganisms. We found a higher prevalence of invasive species in the eastern and southern provinces, compared to the western and northern provinces in China. This pattern is likely due to the differences in the level of economic development and environmental suitability between the two regions. Moreover, with further economic development, China may face more serious biological invasions in the future. These invasions of alien species are largely the combined results of the interactions between the intrinsic traits of these species along with resource opportunities and disturbances by human beings. Many mechanisms are responsible for successful invasions of alien species, but phenotypic plasticity, adaptive evolution, enemy release, interspecific mutualism or commensalism, and new allelochemicals may be primary causative factors. Biological invasions in China have caused serious impacts on native ecosystems, including biodiversity and ecosystem services, alteration of biogeochemical cycles, threats to agricultural and forestry production, traffic and shipping, environmental safety, and public facilities. China has also made progress in the detection and monitoring of invasive species, risk analysis, biological control, radical elimination, and ecological restoration of degraded ecosystems. We suggest several issues that need to be addressed in invasive species research in the future, including territory-wide inventories, evolutionary ecology and genomics, direct and indirect ecosystem-level consequences, interactions between major components of global change and biological invasions, and management and control technologies.
Rapid worldwide urbanization during the last century has led to more than half the world’s population living in urban regions. Studies of how urbanization affects insect diversity have focused on the following: insect abundance, distribution, extinction, food habits and ecosystem services. Native insect populations have declined greatly in urban areas, where studies of their spatial distribution have revealed that abundance decreases along what is termed the rural-city center gradient (RCG), many native insects even extinct with urbanization process. Most specialist insect communities have declined in abundance due to urbanization, while some generalist species, such as aphids, cockroaches and termites, have increased slightly in abundance. It is also the case that herbivorous, parasitic, saprophagous and flower-visiting insects are much more negatively influenced by urbanization than predator insects. This has a significant effect on the ecosystem services of insects. The decline of many insects due to urbanization can be attributed to environmental pollution (including air pollution, water pollution, light pollution, and heat pollution), habitat fragmentation, road hardening, clustering of buildings, and occurrence of introduced invasive species. As urbanization continues, measures should be taken to protect insects in urban areas. This will entail improving basic scientific research on the problem, construction of suitable habitats, and informing the general public of the benefits of environmental protection.
Figs (Ficus, Moraceae) constitute one of the greatest genera of flowering plants with ca. 750 species worldwide. Figs and fig wasps form an obligate specific mutualism, which is treated as the model system to study comparative biology of mutualism and co-evolution. This extraordinary system has received increasing attention because of its specificity and the development of the molecular technologies, although the phylogenetic reconstruction of both partners began in the 1990’s. In this paper, we summarized the research on phylogenetic relationships and fig-fig wasp co-evolution. We also analyzed interrelated researches in China and the future developing trends in research on this mutualism.
Crocus alatavicus, a geophytic-geocarpic plant, is an early spring ephemeral species that grows in subalpine areas of the western Tianshan Mountains. To understand the ecological significance of geocarpy in plants, we studied the breeding system and pollination biology of C. alatavicus, with special reference to its adaptive strategies for a subalpine existence. We found that C. alatavicus is hysteranthous and its flowering pattern was explosive at the population level. It began to flower in early- to mid-April, and the white flowers had neither nectar nor scent. The inferior ovary was below ground at anthesis, while the other floral parts were aboveground. The flowers were open during the day and closed at night, and individual flower duration was 6-9 days. Pollen viability was 75.39±5.69% at the end of anthesis, and stigma receptivity lasted eight days. Results of artificial pollination experiments suggested that the breeding system ofC. alatavicusis facultative xenogamy with the ability to self-pollinate spontaneously. Crocus alatavicushas a generalist pollination system, with Bombus lucorum, Anthophora senilis and Andrena capillosa being effective pollinators. These insects initiated pollination while foraging for pollen, and their visitation frequencies were 0.50±0.27, 0.18±0.08 and 0.13±0.05 per flower per hour, respectively. Thus,C. alatavicusnot only has evolved unique flowering pattern and generalist pollination system, but also utilizes an otherwise vacant niche in the early spring to improve the effectiveness of pollination. Furthermore, characteristics of its breeding system, such as self-compatibility and spontaneous self-pollination, ensure reproductive success even when pollinators are scarce and pollinator visitation frequencies are low in early spring.
Mutualism, or a mutually beneficial interaction between two organisms, are ubiquitous in ecological systems. However, some “empty flowers”, which offer pollinators no any kinds of rewards, design different strategies to attract pollinators without providing rewards to the pollinators. These pollination mechanisms are called deceptive pollination. The family Orchidaceae, representing one of the largest groups in angiosperms, is distinguished by high floral diversity and intricate adaptations to pollinators. Darwin described and identified most of the functional floral morphology and biomechanics in orchid pollination. However, he never recognized that many of the flowers that he examined lacked food rewards for pollinators. Floral evolution in the Orchidaceae appears to be dominated by modes of deceptive pollination, and more than one third of orchid species are thought to be pollinated by deceit. Deceptive pollination is thought to be one of key roles which has lead to relatively high species diversity within the Orchidaceae. Deceptive orchids frequently exploit the food foraging, sexual, oviposition and sleep/warmth behaviors of insects. The most common deception mechanisms include generalized food deception, Batesian floral mimicry, sexual deception, brood-site imitation and shelter imitation. Additionally, floral color, morphology and fragrance play key roles to cheat target pollinators. Relationships between deceptive orchids and their pollinators possibly involve asynchronous evolution; therefore orchids track the diversification of their pollinators. However, deception has negative impacts on the pollinators, which may exert selection on the pollinators. Because duped pollinators tend to avoid rewardless flowers, deceptive orchids suffer low visitation rates and fruit set, various environment factors can affect the reproductive success of these orchids. Deceptive orchids depend largely on insect pollinators for reproduction, and the proclivity of these species to use deceptive pollination strategies puts many of these species at a relatively higher rate of extinction. Therefore, pollination biology studies are needed to provide a scientific basis for proper conservation of orchids. At the community level, co-occurring mimic, non-mimic, and mimic signal providing plant species affect the reproductive fitness of orchids. Therefore, it is necessary to further study the co-evolution webs of deceptive orchids and pollinators along with other related biological and ecological factors.
In agro-ecosystems, habitat loss and fragmentation may alter insect assemblages such as ladybug beetles and aphids, potentially affecting important ecological interactions. We used an experimental model system (EMS) with multiple micro-landscapes in which the habitat loss and habitat fragmentation impacts were distinguishable to test the following hypotheses: (1) Habitat removal results in short-term increases in population density in remaining habitat patches (crowding effect); (2) For the same total habitat area on a landscape, insect density will be higher in landscapes with more but smaller patches and more habitat edge than in less fragmented landscapes; (3) This positive effect of fragmentation on density is larger in landscapes with small inter-patch distances, and these last two effects on colonization should be reduced or disappear over time following habitat removal. This EMS included 18 fragmented and 18 clumped experimental plots. Alfalfa was cut to 1 m×1 m patches in fragmented plots (H=1) and retained the whole patches in continual plots (H=0). Habitat loss was designed to 90%, 80%, 70%, 50%, 20% and 0% respectively. Every plot was 3 times replicated and 0% of habitat loss was CK. Net sweeping, barber traps and clapper boards were used to investigate insect species in experimental alfalfa landscapes. 38 species were divided into 4 groups and diversity and abundance of every group were caculated and the relationship between diversity and habitat loss was analyzed. In our EMS, there was little support for the threshold phenomenon or for general effects of habitat loss and fragmentation, although this conclusion needs to be tempered by the limited duration of the experiment. We observed no threshold in species loss after habitat fragmentation and habitat loss in experimental alfalfa landscapes. The species number in fragmented habitat was higher than that in continual habitat under the same degree of habitat loss. Insect abundance was lower in micro-landscapes with 80-90% habitat loss than in CK. As for species, individuals in fragmented habitat were higher than that in continual habitat under the same degree of habitat loss. Insect diversity did not differ among variously treated micro-landscapes. It appears that insect colonization is low in micro-landscapes with 80-90% habitat loss; species richness, abundance and diversity were all significantly lower than that in CK, especially in fragmented habitats. Herbivorous species appear to colonize more rapidly than predatory species after habitat fragmentation and loss in experimental alfalfa landscapes. Our results did not support our first, but provided some support for the other two hypotheses. We suggest that fragmentation decreased the rate of immigration to patches, resulting in lower population densities in more fragmented landscapes. These results could be used to guide spatial and temporal aspects of the design of agricultural systems in order to enhance natural predator populations in agricultural landscapes and suppress pest population to the greatest extent.
In 2008, an ice storm caused extensive damage to the montane evergreen broadleaved forest in Chebaling National Nature Reserve, Guangdong Province, China. To assess the response of soil arthropod diversity and distribution to a gradient of canopy openness following the ice storm, 17 plots, each 400 m2, were selected within a 2-ha permanent plot. Canopy openness was estimated with hemispherical photography in each plot. We sampled the litter layer and two soil layers (0-10 cm and 10-20 cm) to measure arthropod diversity and soil properties. We used two-way cluster analysis to group sites based on arthropod abundance in the litter layer. We also utilized canonical correspondence analysis to reveal relationships between soil arthropods in the 0-10 cm layer and four environmental variables, i.e., canopy openness (CO), soil organic matter (SOM), electric conductivity (EC), and natural moisture content (NMC). Results showed that abundance, richness and diversity of arthropod communities decreased with depth. A negative association was found between canopy openness and the number of arthropod groups in the litter layer; some arthropod taxa, such as the Oribatida, Prostigmata and Mesostigmata, were found in a wide range of light conditions, whereas the Hymenoptera, Symphyla, Pseudoscorpiones and Lepidoptera larvae may be photophobic. The distribution of arthropods in the 0-10 cm soil layer was closely related to CO, SOM, EC, and NMC on the first and second canonical axes. Hence, a series of changes in canopy structure and soil factors following the ice storm appeared to have affected the composition and distribution of soil arthropod communities. Findings from the present study also indicated that arthropod communities could serve as indicators to characterize the ecosystems they inhabit, thus being particularly suitable for monitoring forest regeneration and successional dynamics following ice storms.
The Three Parallel River Region is an epicentre of Chinese biodiversity, which is reputed as one of the world’s 25 major “biodiversity hotspots”. However, few study has been done on the notorious mosquitoes in this area. We surveyed the mosquitoes in relation to latitude and elevation along the Lancang River (24°-30°N, 1,000-3,500 m asl). Adult mosquito samples were captured using UV light traps from July to September 2005 in the mountainous residential areas. A total of 76,458 adult mosquitoes were collected and identified as 36 species of 5 genera in 2 subfamilies. The results showed: (1) species richness gradually decreased with the increasing latitude but showed a single-peak curve pattern along the altitudinal gradient; (2) α diversity decreased first and then increased slightly along the increasing latitude, showing a wave-like curve along the altitudinal gradient; (3) β diversity (Cody index) was higher in the transitional climate zones, and the same pattern was found along the altitudinal gradient, which reflected the influence of geographical environment and climate on the species composition, fauna and diversity distribution pattern of mosquitoes; (4) Mosquito species were classified into three main ecological types by cluster analysis, namely Oriental fauna, Palaearctic fauna, and the transitional fauna between them; and (5) the result from canonical correspondence analysis indicated that precipitation is the key factor influencing spatial distribution pattern of mosquito diversity in the study area.
The B biotype of Bemisia tabaci, sometimes called a “super bug”, has been one of this species complex’s most harmful biotypes because of the tremendous damage it inflicts worldwide. Recently, competitive displacement of pre-existent biotypes and other herbivores by the B. tabaci B biotype has been observed in many regions worldwide. Based on literature review, the mechanisms responsible for competitive replacement by B. tabaci may include exploitation or interference competition, which involve niche competition, differential abilities in resource acquisition, asymmetric mating interactions, heat shock adaptation, pesticide susceptibility, and interactions between B. tabaci B biotype, host plants, and viruses. Moreover, the B biotype likely has unique endosymbionts, which may be important in enhancing its competitive ability. We also discuss related mechanisms involved with serious damage caused by the B. tabaci Q biotype.
To evaluate the potential role of an urban wetland park in conserving biodiversity during urbanization, we studied ground beetle (Carabidae) diversity using pitfall traps in five vegetation types, i.e., poplar, cypress, mixed forest, barberry scrub, and reed beds, within a newly-built urban wetland park, Cuihu Wetland Park in Beijing, for three years. A total of 441 individuals representing 30 species and 18 genera of carabid beetles were captured. Carabid species richness and abundance both sharply increased with park age. For each of the five vegetation types, approximately 25% of their carabid species (3-4 species) were unique and were not detected in other types. Poplar forest exhibited the highest abundance and richness of carabid species and showed the strongest increasing trend through time. Our results suggested a significant role of urban wetland parks in the conservation of carabid beetle diversity in the process of urbanization. In order to maximize their conservation value, they should be revegetated by a diversity of plants while using poplars as pioneers.
In the fig-fig wasp reciprocal mutualism, understanding mechanisms of coexistence between pollinating wasps and non-pollinating wasps is an important and relevant topic. Niche partitioning has widely been considered as the most important mechanism in the coexistence of pollinating and non-pollinating wasps. In this study, we experimentally examined the diet of five species of non-pollinators and the relationship among fig wasps in Ficus racemosain Xishuangbanna, southern China, from Dec. 2006 to Jun. 2007. Platyneura testacea and P. mayri are gall-makers, but oviposit sequentially, utilizing different female flowers at different developmental stages; Apocryptasp., A. westwoodi and P. agraensis are parasitoids of P. testacea, P. mayri and Ceratosolen fusciceps respectively, presenting species-specific relationships with the hosted species. Species correlation coefficients differed greatly among seasons and conditions, suggesting that the use of correlation analysis to deduce or identify relationships between species in previous studies may be of limited value. Pollinators were the dominant species at our study sites. In these conditions, non-pollinating wasps exist at relatively low population density, and therefore may have a weak impact on the stability of the mutualism, potentially enabling the non-pollinating wasps coexist with the mutualism between figs and fig wasps.
Mutualism is one of the most important ecological interactions, with strong influences on almost all levels of biological systems. Their long-term persistence raises many challenging evolutionary questions, especially those involving high-level coevolution and coadaptation. Figs and their pollinating wasps are among the most tightly integrated mutualisms known, and provide a model system for developing and testing theories of coevolution. Initial studies suggested specific coevolution between them, described as the famous rule of one fig one wasp. However, more and more exceptions have been revealed by recent studies, and cryptic species in pollinating wasps and host switching were found common in some regions and within some Ficus groups, inducing debates on the levels of species specificity and coevolution. A broad-sense coevolution model to describe the relationship of the related groups of figs and their pollinating wasps was proposed recently. The diverse relationships between figs and their pollinating wasps indicated coexistence of both specific and diffuse coevolution in this mutualism system, producing different species-specificity level. However, which model is the dominant one in this system is still keeping open. The species specificity could be tight or loose in different regions and fig groups involved. Consequently, the frequencies and mechanisms of breakdowns of the one-to-one rule within different fig groups as well as in different regions are essential for the understanding of the relative importance of the competing finer-scale cospeciation or broad-sense coevolution models.
Variable insect behaviors may result in different flower visiting frequencies, which may result in diverse impacts on plant pollination. Although flies, hoverflies, and Italian bees (Apis mellifera ligustica) were the most common visitors of Chimonanthus praecox, these insect groups had disparate visiting behaviors. Flies traveled quickly, and crawled or jumped between flowers. Italian bees also flew quickly or occasionally crawled between flowers. In contrast, hoverflies generally spent a majority of time foraging on a given flower. Based on the average foraging time and inter-floral flight time, one Italian bee could visit 4.57 flowers per minute, whereas individual bees and hoverflies could visit 2.65 and 0.53 flowers on average, respectively. After incorporating the total number of individuals for each insect group, we extrapolated the visiting rates of Italian bees, flies and hoverflies as 498.19, 1,089.74 and 99.78 flowers per minute, respectively. Flies and Italian bees had higher pollination effectiveness (number of pollinated flowers by the same number of visitors in a given time interval under the same condition), with estimates of 93% and 100% (n = 30), respectively, while only 13% (n = 30) for hoverflies. If we consider the pollen load ability and pollination effectiveness for Italian bees and flies, visiting rate may be the main limiting factor for their potential in pollinating flowers. Thus following these conclusions, flies are the major pollinators of C. praecox, followed by Italian bees (pollination role was limited by their low number) and hoverflies (limited by their foraging and hovering behaviors and lower pollination effectiveness).