国内外船舶压载水处理技术的发展现状

由于船舶压载水的不处理排放使得病原体、海洋有害生物在大海中肆意传播,对海洋物种的生存造成了压力。有关数据显示,由于船舶载压水造成的外来物种已经达到500余种,并且数量还在增加,科学家将船舶压载水引起的外来生物入侵列为未来海洋面临的重大危机。文章研究了国内外压载水处理系统的发展,并针对主流技术进行了分析,为船东选择压载水技术提供导向。     

海洋外来物种入侵生态学研究

海洋外来物种入侵已成为最为严重的全球性环境问题之一。海洋生态系统类型多样、环境复杂,其生物入侵的监测、控制与管理难度相对较大。我国对陆地外来生物的入侵已开展了较为深入的研究,但对于海洋外来生物的入侵研究仍处于起步阶段,对其入侵监测、入侵机制、入侵危害的程度以及防治等问题缺乏基础数据。本文在分析国内外海洋外来生物入侵现状的基础上,概述其入侵生态学研究形势及相关成果,包括海洋外来物种的入侵途径、入侵过程、入侵生态效应以及全球变化对入侵的影响等。海洋外来生物的入侵可能对海洋生态系统造成直接或间接的影响,如种间竞争破坏生态环境、与土著种杂交造成遗传污染、病原生物及有毒藻类导致海洋生态灾害加剧等。此外,从政策和法规、入侵风险评估、监测和公共宣传教育、生物信息系统和有效管理机制等方面提出对我国海洋外来物种入侵的防治策略。本研究为我国海洋外来物种的进一步研究提供了参考。     

广西外来入侵植物

通过调查和文献整理,初步确认广西有外来入侵植物114种,隶属于36科80属,其中以菊科的种类最多,有26种。外来入侵植物来源于世界各地,以来源于美洲居多,有87种,占76.3%。入侵植物以草本植物为主,有90种,占78.9%。外来入侵植物主要通过有意引入和无意传入等方式入侵广西。它们的入侵,特别是一些恶性杂草的入侵,给广西农业、林业、人类健康以及生态环境带来巨大的负面影响。加强对外来入侵植物的调查和评估,恢复当地植被和物种的多样性,开展有害生物风险分析是防范外来入侵植物的有效途径。     

外来入侵物种管理中的排序体系研究进展

外来物种入侵是继生境破坏之后的第二大世界性的环境问题, 如何实现外来入侵物种分级, 对其进行有效管理是一个世界性的难题。研究总结了国内外外来入侵物种的排序体系, 从三个方面归纳了目前的排序系统: 1)针对所有入侵以及潜在入侵物种开展综合风险评估, 以此为基础提出防控管理清单; 2)针对已建群的外来入侵物种, 围绕不同管理目标进行入侵物种的排序, 包括以降低外来入侵物种对生物多样性影响为目的的外来植物排序、以生物防治为控制手段的外来物种排序、基于土地利用的种群管理排序; 3)针对区域管理提出外来入侵物种分区管理。认为外来入侵物种的入侵性、生态危害、分布范围、潜在分布和控制技术是实现排序的关键因素, 指标的选择与确定依赖于管理目标的设定。我国亟需确定外来入侵物种的优先控制区域, 并针对不同优先控制区域内外来入侵物种开展排序工作。     

动物入侵的行为机制

行为特征可在外来动物建立种群和扩张过程中发挥重要作用,因此,要正确理解动物入侵,常常需要仔细研究其行为机制。20世纪80年代以来,随着动物入侵规模在世界各地的迅速加剧,有关其行为机制的研究也受到了广泛关注。最近一些研究表明,一些入侵动物种内攻击和觅食等行为具有可塑性,因此它们能够灵活应对多变的环境条件,这对于种群的建立和维持至关重要;入侵动物与土著物种发生行为互作时,往往占据优势,从而取代土著物种,并有助于其地域扩张;入侵动物长距离扩散可以提高其地域扩张速度,许多行为可与扩散行为结合进一步促进扩张。今后需要加强对入侵动物的行为分析,使之全面地融合到生物入侵的研究之中。这不仅可以提高对外来物种入侵的预警和治理能力,而且为探索动物行为的奥秘以及动物间行为互作在物种进化中的意义提供了独特的机会。     

外来入侵植物成灾的机制及防除对策

外来入侵植物是指自然或人为地由原生态系统中引入到新生境的植物 ,会给新生境或其中的物种带来威胁。紫茎泽兰从缅甸自然进入云南 ,其原产地是墨西哥 ;水葫芦从墨西哥引进用作饲料 ,而大米草是从英国南海岸引入用于促淤护堤。 3种外来入侵植物给我国当地的生产、生活等带来了极大的威胁 ,破坏了生态系统 ,影响了生物的多样性。对它们的治理费用昂贵。其繁殖力、适应性和抗逆性极强 ,竞争力也极强或本身拥有化感特性或特殊器官 ,同时又耐瘠、耐污 ,并且在本地还缺乏有力的竞争生物和天敌 ,是 3种外来入侵植物势不可挡 ,扩散蔓延的成灾机制。致力于外来入侵植物的国家能力建设和综合治理是 3种外来入侵植物的防除对策     

竞争和景观格局相互作用对外来入侵物种传播影响的动态模拟

通过中性景观模型和元胞自动机模型模拟了不同景观格局、不同竞争力和关键种群特征的外来入侵物种的传播动态,模拟结果表明:(1)竞争力强的外来入侵物种,可利用生境面积越大,集聚度越高,越有利于其入侵和传播,而对竞争力弱的外来入侵物种来说,可利用生境面积越小,越分散,越有利于其生存。竞争力强可以有效利用整块的高集聚度的资源,而弱竞争力的外来入侵物种为了逃避土著种的竞争往往趋向于分布在分散的小生境中;(2)可利用生境面积大于50%时,景观格局集聚度越小,竞争力弱的外来入侵物种适应环境的弛豫时间越长;(3)外来入侵物种的传播与种子产量呈正相关关系,与繁殖年龄呈负相关关系,拟合关系因景观格局和竞争而异;(4)平均迁移距离对外来入侵物种传播的影响最大,在管理过程中应根据不同的目标,不同的景观格局、竞争力和种群特征选择合适的管理措施。     

“世界100种恶性外来入侵物种”在我国大陆的入侵现状

[目的] 明确世界自然保护联盟公布的“世界100种恶性外来入侵物种”在我国大陆发生分布现状,为我国制定外来入侵物种管控对象和分级管理对策提供依据。[方法] 基于在线数据库系统、文献报道以及外来入侵物种本底调查结果,采用分类统计方法,对物种的分类地位、原产地、在我国的入侵状态及其所在的生态系统进行分析。[结果] 世界100种恶性外来入侵物种已有82种在我国发生分布,包括本地种33种、外来入侵种32种、外来非入侵种16种,以及未明确入侵状态1种。其中,32种外来入侵种包括陆生无脊椎动物8种、哺乳动物2种、鱼类2种、两栖动物1种、爬行动物1种、水生无脊椎动物2种、陆生植物9种、水生植物4种、真菌1种、卵菌1种和病毒1种。以上物种主要分布在东南沿海地区和西南地区,而较少分布在西北地区和东北地区;约75%物种分布在农田、城镇、森林和湿地4类生态系统。[结论] 建议外来入侵物种管理部门重点关注尚未在国内发生分布的18种潜在外来入侵物种,并列入国家外来入侵物种相关管理对象,严防其传入与扩散;严密监控国内已发生且具有潜在危险的外来物种,防止其向可能入侵的生态系统边缘扩散;继续对在国内已发生的外来入侵种实施区域性分级控制管理措施。     

分子标记技术在入侵生态学研究中的应用

外来入侵物种给农林业生产造成了巨大的经济损失,并威胁生物多样性及人类健康．入侵生态学的研究对于认识外来入侵物种的入侵机制及其可持续控制具有重要意义．分子标记技术为解决入侵生态学研究中的许多基本问题提供了良好的手段．本文综述了该技术在外来入侵物种的鉴定、地理分布、原产地、传播模式、种群遗传变异、杂交及基因渗入等研究中的应用现状,并对其应用前景进行了展望．     

浅议我国外来物种入侵问题及其防治对策

随着世界经济的发展和全球经济一体化进程的加快,外来物种入侵已成为影响国家安全的主要因素之一。我国外来入侵物种数量繁多,已成为遭受外来生物危害最严重的国家之一,入侵物种已对我国生态系统、环境和社会经济造成了严重的影响。近年来,各国都积极采取措施,制定外来物种入侵管理政策,加强外来物种入侵立法,确保国家及国际生物安全。然而,我国现有的针对外来物种的相关法律法规存在明显滞后。本文综述了我国外来物种入侵的现状及相关立法,指出外来物种入侵可在不同生态系之间发生,揭示了行政区划与生态系差异造成外来物种入侵管理存在"自然与经济的错位"、国内管理方面存在"生态系统与行政区域的错位"的"双错位现象",分析了我国外来物种的管理现状及今后的发展方向,以期探求我国在国际背景下的外来物种管理对策,提出制定《外来入侵物种法》及相关法律的国家体系、建立跨部门协作科学研究体系以及建设行政管理体系,增强抵御外来物种入侵的能力,实施以防为主的管理策略。     

Molecular detection of native and invasive marine invertebrate larvae present in ballast and open water environmental samples collected in Puget Sound

Non-native marine species have been and continue to be introduced into Puget Sound via several vectors including ship's ballast water. Some non-native species become invasive and negatively impact native species or near shore habitats. We present a new methodology for the development and testing of taxon specific PCR primers designed to assess environmental samples of ocean water for the presence of native and non-native bivalves, crustaceans and algae. The intergenic spacer regions (IGS; ITS1, ITS2 and 5.8S) of the ribosomal DNA were sequenced for adult samples of each taxon studied. We used these data along with those available in Genbank to design taxon and group specific primers and tested their stringency against artificial populations of plasmid constructs containing the entire IGS region for each of the 25 taxa in our study, respectively. Taxon and group specific primer sets were then used to detect the presence or absence of native and non-native planktonic life-history stages (propagules) from environmental samples of ballast water and plankton tow net samples collected in Puget Sound. This methodology provides an inexpensive and efficient way to test the discriminatory ability of taxon specific oligonucleotides (PCR primers) before creating molecular probes or beacons for use in molecular ecological applications such as probe hybridizations or microarray analyses. This work addresses the current need to develop molecular tools capable of diagnosing the presence of planktonic life-history stages from non-native marine species (potential invaders) in ballast water and other environmental samples.     

Transport of diatom and dinoflagellate resting spores in ships' ballast water: implications for plankton biogeography and aquaculture

Diatom and dinoflagellate species that are not endemic to aregion can be inadvertently introduced when their resistantresting stages are discharged with the ballast-tank waters andsediments of bulk cargo vessels. A survey of 343 cargo vesselsentering 18 Australian ports showed that 65% of ships were carryingsignificant amounts of sediment on the bottom of their ballasttanks. All of these samples contained diatoms, including speciesthat are not endemic to Australian waters. Diatom resting spores,especially of Chaetoceros, were also detected. Dinoflagellateresting spores (cysts) were present in 50% of the sediment samples.Of the 53 cyst species identified, 20 (including Diplopelta,Diplopsalopsis, Gonyaulax, Polykrikos, Protoperidinium, Scrippsiellaand Zygabikodinium spp.) were successfully germinated to produceviable cultures. Such diversity of diatom and dinoflagellatespecies in ships' ballast water suggests that the apparent cosmopolitanismof many coastal phytoplankton species may be due partly to theglobal transport of seawater ballast. Of considerable concernwas the detection in 16 ships of cysts of the toxic dinoflagellatesAlexandrium catenella, Alexandrium tamarense and Gymnodiniumcatenatum. One single ballast tank was estimated to contain>300 million viable A.tamarense cysts, some of which weresuccessfully germinated in the laboratory to produce toxic cultures.These toxic dinoflagellate species, which can contaminate shellfishwith paralytic shellfish poisons, pose a serious threat to humanhealth and the aquaculture industry. Ballast-water quarantinemeasures recently introduced in Australia are discussed. Mid-oceanexchange of ballast water is only partially effective in removingdinoflagellate cysts which have settled to the bottom of ballasttanks. The present work indicates that the most effective measureto prevent the spreading of toxic dinoflagellate cysts via ships'ballast water would be to avoid taking on ballast water duringdinoflagellate blooms in the water column of the world's ports.     

A biological survey of ballast water in container ships entering Hong Kong

The role of ballast water in the introduction of exotic species has recently received extensive attention. The aim of this study is to assess the importance of ballast water discharge as a vector for the introduction of exotic species into Hong Kong waters. Twelve ballast water samples were collected from 5 container ships entering Hong Kong between June1994 and October 1995. The ballast water originated from ports on both sides of the Pacific Ocean. At least 81 species from 8 animal phyla and 5 protist phyla were found. Most of the major marine taxonomic groups were represented and many planktonic larval stages were included. Species richness in the ballast tanks decreased with the age of ballast water. Copepoda was the most diverse and abundant taxonomic group. The density of calanoid and cyclopoid copepods decreased with the age of ballast water, but that of harpacticoid copepods did not change significantly with time. Bivalve, crustacean, polychaete and ascidian larvae from ballast water samples were observed to settle in laboratory culture tanks. The mussel Mytilopsis sallei which was introduced to Hong Kong in 1980, was one of the bivalves that settled readily. Results of this study indicate that ballast water can be a major source for the introduction of exotic species to Hong Kong waters. Regulatory guidelines on the discharge of ballast water should be established. This revised version was published online in August 2006 with corrections to the Cover Date.     

Diatom survivorship in ballast water during trans-Pacific crossings

Ship ballast water is believed to be responsible for global dispersal of alien biota; mid-ocean ballast water exchange is most commonly used to mitigate this process. Diatoms are among the most abundant biotic-component in ballast water, yet their invasive biology is poorly understood. To test effectiveness of MOE we examined diatom species composition and cell density in two sets of samples. First, we examined samples collected daily during one 24 days long trans-Pacific crossing in tanks with and without ballast exchanged. Second, we used samples from 23 trans oceanic vessels arriving at Vancouver harbour where diatoms were collected on arrival. Up to 86,429 live diatom cells/l were found in the tanks, ~50% of the samples share up to eight species consistently present. Cell densities and species richness declined over time and with replacement of coastal ballast water by mid-oceanic water. In both data sets diatoms survive in the tanks for as long as 33 days despite ballast exchange.     

Dynamics and short-term survival of toxic cyanobacteria species in ballast water from NOBOB vessels transiting the Great Lakes—implications for HAB invasions

We measured the presence, viability and potential toxicity of cyanobacteria in ships’ ballast tanks during three domestic voyages through the North American Great Lakes. Using molecular methods, the toxin-producing forms of Microcystis and Anabaena were monitored in ballast water after ships’ ballast tanks were filled at their first port of call, and at subsequent ports as ships transited the Great Lakes. Microcystis was detected in ballast water at intermediate and final ports of call in all three experiments, but the presence of Anabaena was more variable, suggesting low abundance or patchy distribution in ballast tanks. Both species were detected in ballast water up to 11 days old. Detection of the microcystin synthetase gene, mcyE, in ballast tanks indicated entrained cells were capable of producing microcystin, and further analyses of RNA indicated the toxin was being expressed by Microcystis, even after 11 days in dark transit. These data demonstrate within-basin transport and delivery of planktonic harmful algal bloom (HAB) species to distant ports in the world's largest freshwater reservoir, with potential implications for drinking water quality. These implications are discussed with respect to management of microbial invasions and the fate of introduced phytoplankton in their receiving environment.     

The efficiency of regional ballast water exchange: Changes in phytoplankton abundance and diversity

Ballast water was sampled on 12 occasions before and after an exchange process carried out in regional seas in order to assess the efficiency of this type of ballast water management at reducing the abundance and diversity of phytoplankton. Although there was an overall reduction in the average abundance and number of taxa after exchange this was not consistent between tanks and voyages. On some occasions there were changes in species composition after exchange and, in some cases, there were increases in potentially harmful species after the exchange process. Factors such as the depth of the water during the exchange process, the season and the method of exchange influenced the efficacy of the exchange process. The variability in the results after exchange mean that this is unlikely to be a ballast water management method that would give consistent results and careful consideration would have to be given to the suitability of using this method in regional seas as a means of reducing the risk of introducing non-native species.     

Flow cytometry, microscopy, and DNA analysis as complementary phytoplankton screening methods in ballast water treatment studies

Ballast water is the main vector for marine invasions. To minimize the spread of invasive species, the International Maritime Organization (IMO) has adopted the Ballast Water Management Convention which requires the installation of shipboard ballast water treatment systems (BWTS). During BWTS tests, the phytoplankton abundance and species composition were followed after treatment with both filtration and ultraviolet radiation. Although the installation fulfilled the IMO criteria after a 5-day holding time in a model ballast tank, the ultimate effectiveness of the treatment was further tested in long-term (20 days) incubation experiments under optimal phytoplankton growth conditions. Application of flow cytometry, microscopy, and DNA sequencing to these incubation samples gave an indication of the phytoplankton species that might be introduced by ballast water discharge—despite treatment. Phytoplankton was reliably quantified using flow cytometry, while fast identification was best done using microscopy. Some groups that contained potentially toxic species could not be identified at species level using microscopy; for these species, identification using genetic techniques was necessary. It is concluded that if long-term incubation experiments are used as an additional tool in testing BWTS effectiveness, a combination of phytoplankton screening methods can be applied depending on the detail of information that is required.     

Reflections on the ballast water dispersal—harmful algal bloom paradigm

The ballast water dispersal—HAB paradigm, increasingly invoked circumstantially to explain puzzling and unaccountable HAB species outbreaks when lacking the multiple tests of confirmation recommended by Bolch and de Salas (2007), is evaluated. The types and examples of natural dispersions and taxon cycles are compared to exotic species bloom behavior linked to ballast water vectoring. The regional spreading, bloom behavior and disjunct distributions of the brown tide pelagophyte Aureococcus anophagefferens and the toxic dinoflagellate Gymnodinium catenatum, attributed to ballast water vectoring, are used as representative examples to evaluate the general application of the ballast water—HAB paradigm and associated interpretative problems. Human-aided emigration has a seeding and colonization ecology that differs from bloom ecology. For self-sustaining blooms to occur, these two ecologies must be accommodated by habitat growth conditions. The three stages that a non-native species must pass through (pioneering, persistence, community entry) to achieve colonization, community maintenance, and to bloom, and the niche-related factors and role of habitat disturbance are discussed. The relevance of cryptic occurrences, cyst deposits, dormancy periods and bloom rhythms of HAB species to their blooms attributed to ballast water-assisted introductions is also sketched. The different forms of HAB species rarity, their impact on the ballast water dispersal—HAB paradigm, and the dispersion and blooms of specialist and generalist HAB species are discussed. The remarkable novel and, often, monospecific blooms of dinoflagellate HAB species are being paralleled by similar eruptive bloom behavior cutting across phylogenetic lines, and being found also in raphidophytes, haptophytes, diatoms, silicoflagellates, etc. These blooms cannot be explained only as seeding events. An ecological release of ‘old barriers’ appears to be occurring generally at coastal bloom sites, i.e. something significant is happening ecologically and embedded within the ballast water—HAB paradigm. There may be a relationship between Life Form type [Smayda, T.J., Reynolds, C.S., 2001. Community assembly in marine phytoplankton: application of recent models to harmful dinoflagellate blooms. J. Plankton Res. 23, 447–461] and mode of expatriation; HAB dinoflagellate species commonly reported to produce ballast water-assisted toxic blooms invariably are members of cyst-producing Life Forms IV, V, VI. Ballast water vectoring of Life Forms I, II, III is rarely reported, even though many produce cysts, and where their novel introductions do occur they are more likely to be ichthyotoxic and vectored in shellfish stock consignments. The relevance of, and need to distinguish between morphospecies and their geographic/ribotype clades are discussed based on the Alexandrium tamarense/catenella/fundyense complex. Morphospecies-level ballast water dispersions are probably minor compared to the dispersal of the different ribotypes (toxic/non-toxic clades) making up HAB morphospecies; the redistribution and admixture of genotypes should be the focus. Ballast water-assisted expatriations impact the global occurrence of HABs through the direct transfer of previously absent species or introduction of genetic strains from the donor habitat that are ecologically favored over resident strains. The hybridization of species may be of potentially greater impact, resulting from the (1) mating of individuals from the donor and recipient habitats, or (2) through the interbreeding of strains introduced from two different donor sites into the recipient site, and whose progeny have greater ecological fitness than indigenous strains. Exceptional ecological changes of some sort appear to be occurring globally which, in combination with the genetically altered ecophysiological behavior of HAB species linked to ballast water dispersion and admixture, underpins the global HAB phenomenon. The impact of ballast water and shellfish transplantation on HABs and phytoplankton community ecology, generally, is considerably greater than the current focus on HAB species distributions, vectoring, and blooms. The methodological, investigative and conceptual potential of the ballast water—HAB paradigm should be exploited by developing a GEOHAB type intiative to advance quantification of global HAB ecology.     

Characterization of bacteria in ballast water using MALDI-TOF mass spectrometry

To evaluate a rapid and cost-effective method for monitoring bacteria in ballast water, several marine bacterial isolates were characterized by matrix-assisted laser desorption ionization-time of flight mass spectrometry (MALDI-TOF MS). Since International Maritime Organization (IMO) regulations are concerned with the unintended transportation of pathogenic bacteria through ballast water, emphasis was placed on detecting species of Vibrio, enterococci and coliforms. Seawater samples collected from the North Sea were incubated in steel ballast tanks and the presence of potentially harmful species of Pseudomonas was also investigated. At the genus-level, the identification of thirty six isolates using MALDI-TOF MS produced similar results to those obtained by 16S rRNA gene sequencing. No pathogenic species were detected either by 16S rRNA gene analysis or by MALDI-TOF MS except for the opportunistically pathogenic bacterium Pseudomonas aeruginosa. In addition, in house software that calculated the correlation coefficient values (CCV) of the mass spectral raw data and their variation was developed and used to allow the rapid and efficient identification of marine bacteria in ballast water for the first time.