Distinguishing ecological engineering from environmental engineering

This paper uses complex system thinking to identify key peculiarities of ecological engineering. In particular it focuses on the distinction between the purpose-driven design of structures in environmental engineering and the natural process of self-organization characteristic of life, which needs to be integrated into ecological engineering.Conventional engineering addresses the problem of fabrication of an organized structure, say a road, which reflects a goal at the outset, as well as considerations external to the road. At the outset there is an essence of which the organized structure is a realization. This realization belongs to a certain type (apartment building, suspension bridge). The type is in relation to: (a) the expected contexts (e.g. housing in Manhattan, a bridge in rural Africa) and (b) location-specific socio-economic constraints (low/high economic budget). Conventional engineering does not question the goals of the selected plan and can only object to the feasibility of a proposed typology in a given context. Engineers deal with the challenge of the realization of a plan at a given point in space and time.The central dogma of biology identifies organisms as informationally-closed and this makes possible their use as machines. Ecological systems, on the contrary, are informationally-open. They cannot be used as machines to create functional structures, because they are becoming in time. For engineered structures to work it is usually required that there is (1) stability of system components; (2) admissibility of a workable context; (3) validity of purpose and concept. Ecologically-engineered structures challenge these requirements because of specificity of required environments and lability of system parts over the time the engineered structure functions. Other engineering is better if it achieves flexibility, but ecological engineering must be so flexible as to take on a looping character that updates the system to meet changing requirements. Accordingly, the original goals cannot be taken for granted later in the process of ecological engineering. Ecological engineering has to be a flexible iterative process of design, in which the designer must continually update goals, essences, typologies and processes of realization.     

滩地林业生态工程与钉螺孳生关系的研究

研究表明,草滩钉螺密度与淹水时间呈正相关,淹水时间与林木生长性能呈负相关．淹水期每增加１天,钉螺密度上升２２６９个·ｈｍ－２．滩地实施抑螺林业生态工程３年后钉螺密度下降８４％．     

Integrated ecological engineering of corn utilization in Zhaodong County

Basing on fundamental principles of ecological engineering, the conversion, reuse and recycling of products, by-products, and waste in the processing of corn, straw, cob and root from a certain county have been designed and put into practice. The design is an integration of many techniques including chemical, biological and physical ones suited to local conditions. Some results with a great potential have been obtained.     

An integrated habitat enhancement approach to shoreline stabilization for a Chesapeake Bay island community

Shore protection and habitat enhancement along a residential island werethe main goals of this shoreline study. The physical and geological factorsnecessary to design shoreline stabilization structures capable of confidentlysupporting suitable and stable habitat enhancement/restoration substrate areemphasized since this area of study generally may be unfamiliar to wetlandresource managers. Erosion along the targeted shoreline is influenced by aunidirectional wave field from the south-southwest. Results of our analysesshowthat a headland control system comprised of headland breakwaters could be usedsuccessfully to stabilize the existing shoreline and provide resource managersflexibility in habitat restoration decisions. Headland breakwaters are designedto diffract wave energy so that shore planform equilibrium is attained and canbe sized and positioned to maximize the length of stabilized shoreline.Maximization of the new shoreline length provides increased subaerial,intertidal, and subaqueous environments for flexible habitat restorationalternatives. The final restoration design developed through this study willcreate approximately 69,000 m² of new habitat includingstable beach, dune, tidal marsh, scrub shrub, and submersed aquatic vegetation.An additional 2,000 m² of rock substrate habitat isprovided directly by the headland control structures.     

用生态工程技术控制农村非点源水污染

非点源污染的本质是农村生态系统的严重失调,生态工程技术是进行流域生态修复,强化物质循环的有效方法,非点源污染的治理策略有控制径流污染和控制源头污染两个方面。本文介绍了多水塘系统,植被缓冲带,湿地系统,生态农业、坡面生态工程和污染物生态处理6种生态治理技术,它们的有机结合可形成控制非点源污染的流域生态工程,执行时,应该因地制宜,还要加强资金、管理和教育的投入。     

From a civil engineering project to an ecological engineering project: An historical perspective from the Mont Saint Michel bay (France)

Because of an excess of sedimentation due to natural and anthropogenic causes, the Mont Saint Michel (France) is becoming less frequently surrounded by seawater during high tide events. This prestigious monument and its bay have both been recognized by multiple national and international institutions for cultural and ecological richness. Diverse human activities such as tourism, fisheries, and farming also occupy the Mont Saint Michel Bay. The French government has been faced with a challenge of preserving the integrity of the bay, while restoring the ‘insularity’ of what used to be an island, the Mont Saint Michel. The objective of this paper is primarily to demonstrate how environmental scientists and ecologists influenced a typical civil engineering project and modified it into a civil/ecological engineering project, more respectful of both environment and human interests. To achieve this objective, we first retrace the formation of the Mont Saint Michel Bay, under both geological and historical perspectives, to provide the necessary background for the understanding of the actual restoration project. Some of the first projects that were proposed were designed to destroy the area of salt marshes that surrounded the Mont Saint Michel, with no consideration for the ecological integrity of the site. We conclude by presenting the current project in which France will invest over 130 million USD in the next few years. If this final project cannot be recognized truly as an ecological engineering project, it has the merit of being a compromise between various partnerships which have been debating for more than a century.     

Ecological engineering methods for soil and water conservation in Taiwan

This paper describes the development of Taiwan's localized ecological engineering methods to make the mitigation works more effective. To strengthen the soil and water conservation and protection of the ecological environment, comprehensive mitigation planning is necessary with considerations that include balancing the safety, ecology, and landscape, and treating the whole watershed as a unit. To demonstrate the achievement of the promotion of the ecological engineering methods in Taiwan, this paper illustrates two complete mitigation examples for a debris flow torrent and a stream. Most of the mitigation works have survived and are still stable (with some minor damages) after the two strong typhoons of 2004. We show that the developed ecological engineering methods are very suitable in mitigation and worthwhile for further promotion for Taiwan's ecological environment.     

Effect of ecological engineering on the nutrient content of surface sediments in Lake Taihu, China

Ecological engineering was carried out in Meiliang Bay of Lake Taihu beginning in 2003 in order to improve water quality. There were two main objectives: to improve the growth environment for macrophytes, and to restore macrophyte assemblages. We examined surface sediments once per month beginning in April 2005 to study the response of sediment nutrient content to the ecological engineering. Average total nitrogen (TN) and total phosphorus (TP) concentrations in the surface sediments were 7043 and 1370 mg kg⁻¹, respectively, in May 2005, while after 1 year, TN concentration was reduced to 2929 mg kg⁻¹ and TP concentration was reduced to 352 mg kg⁻¹. We conclude that ecological engineering can lower the nutrient content in surface sediments when it is used to improve water quality.     

Emergence and development of agro-ecological engineering in China

Chinese agricultural eco-engineering is a newborn scientific field which emerged in the practices of sustainable development of agriculture. Based on the discussion of the emergence and development of China’s agricultural eco-engineering, this paper analyzes the characteristics and components of the system. As a case study, the paper introduces the application of ecotechnology and its comprehensive effect in Baiquan county, Helingjiang province, China.     

Engineering novel habitats on urban infrastructure to increase intertidal biodiversity

Urbanization replaces natural shorelines with built infrastructure, seriously impacting species living on these “new” shores. Understanding the ecology of developed shorelines and reducing the consequences of urban development to fauna and flora cannot advance by simply documenting changes to diversity. It needs a robust experimental programme to develop ways in which biodiversity can be sustained in urbanized environments. There have, however, been few such experiments despite wholesale changes to shorelines in urbanized areas. Seawalls––the most extensive artificial infrastructure––are generally featureless, vertical habitats that support reduced levels of local biodiversity. Here, a mimic of an important habitat on natural rocky shores (rock-pools) was experimentally added to a seawall and its impact on diversity assessed. The mimics created shaded vertical substratum and pools that retained water during low tide. These novel habitats increased diversity of foliose algae and sessile and mobile animals, especially higher on the shore. Many species that are generally confined to lowshore levels, expanded their distribution over a greater tidal range. In fact, there were more species in the constructed pools than in natural pools of similar size on nearby shores. There was less effect on the abundances of mobile animals, which may be due to the limited time available for recruitment, or because these structures did not provide appropriate habitat. With increasing anthropogenic intrusion into natural areas and concomitant loss of species, it is essential to learn how to build urban infrastructure that can maintain or enhance biodiversity while meeting societal and engineering criteria. Success requires melding engineering skills and ecological understanding. This paper demonstrates one cost-effective way of addressing this important issue for urban infrastructure affecting nearshore habitats. Electronic supplementary material  The online version of this article (doi:) contains supplementary material, which is available to authorized users.     

湖泊富营养化治理的生态工程

1996年对长春南湖的富营养化实施了生治理工作,调查结果表明,通过收获水生高等植物和鱼产品带出湖体的P量分别为149．6和189．9kg,通过蚌体生长固定的P量为153.4kg,三者合计492.9kg,与湖体会年P输入量大体持平,生态工程运转后,水质明显好转,湖水中的总P浓度逐年下降,浮游植物个体密度减小,种类数增加,生态工程是城市湖泊富营养化治理较为理想的方法。     

Species richness,composition, and abundance of fish larvae and juveniles inhabiting natural and developed shorelines of a glacial Iowa lake

Synopsis Young-of-the-year fish communities in naturally vegetated sites were compared with those inhabiting nearby sites where lakeshore development (i.e., construction of homes, boat docks, and beaches) reduced nearshore macrophyte species richness and abundance. The study was conducted in a 2266 hectare, glacially formed, eutrophic lake in northwestern Iowa during the summers of 1987 and 1988. Study sites were divided into 3 depth zones, and fishes were collected by seining (0–1 m), plexiglass traps (1–2 m), and a nonclosing Tucker trawl (2–3 m). Species richness and total fish abundance were consistently greater in natural than in developed sites in both nearshore (0–1 m) and intermediate (1–2 m) depth zones, but differed little between natural and developed sites in the offshore (2–3 m) depth zone. Nearly 50% of the species sampled, including yellow perch Perca flavescens and bluegill Lepomis macrochirus, inhabited limnetic areas as larvae before migrating inshore as juveniles. Eighteen of the 20 fish species collected as juveniles were in greater abundance in natural than in developed sites. Smallmouth bass Micropterus dolomieui was the only game species consistently found in equal or greater abundance in developed sites. Within all sites, juvenile fishes were generally most abundant where macrophyte abundance and species richness were greatest. Findings from this study demonstrate the importance of nearshore aquatic vegetation to fishes during their first summer of life. If nearshore vegetation beds of lakes continue to be regarded as a nuisance and indiscriminately removed, important fish nursery habitat will be lost. The short-term result will likely be reduced year-class strength of vegetation-dependent species. More importantly, the long-term effects will be changes in fish community richness and composition which will, in turn, alter the lake's fishery.     

中国米草生态工程的功与过

米草生态工程在我国已经走过40年的发展历程,成为中国海岸线一道绿色长城.米草生态工程曾经发挥了显著的生态效益和经济效益,如保滩护堤、促淤造陆、改良盐土、净化水质等,同时也出现了一些负面作用,如绞杀土著物种、侵占航道、危害贝类养殖等.米草的种群爆发可能是因为富营养化、温室效应以及一些可能的人为因素.对待米草,应该科学分析与对待,在种群爆发地区进行科学防治的同时,还应充分发挥其生态与经济效益.     

Ecological engineering in intertidial saltmarshes

Feedbacks between plant biomass density and sedimentation maintain intertidal marshes in equilibrium with mean sea level (MSL). Stable marshes exist at an elevation that is supraoptimal for the biomass density of marsh macrophytes. At this elevation, biomass density is sensitive to changes in MSL, and adjustments in productivity and sedimentation rate help to maintain the marsh in a dynamic equilibrium with sea level, provided that the surface elevation remains within the supraoptimal range of the vegetation. The equilibrium elevation varies inversely with the rate of sea-level rise and directly with biomass density. It was also shown that a succession of intertidal plant communities depends upon the rate of sea level rise and the distribution of biomass density as a function of hydroperiod. Soft engineering solutions to coastal flooding could incorporate planting of marsh vegetation in the intertidal zone for the purpose of promoting sedimentation and dissipating wave energy. A successful design would employ plant species that have varying degrees of tolerance to flooding, maximum drag at their preferred depths, broad ranges within the intertidal zone, and that form a successional series.     

Remediation of ecosystems damaged by environmental contamination: Applications of ecological engineering and ecosystem restoration in Central and Eastern Europe

To investigate the applicability of ecological engineering to pollution problems prevalent in present-day Central and Eastern Europe, a SCOPE-UNEP sponsored workshop was held in Estonia in November 1995. The workshop was undertaken specifically to obtain information from and to train planners, managers and scientists in the region. These ‘countries in transition' face, in many respects, unique environmental problems as a result of their recent domination by a centralized planning government system. Twenty workshop findings that resulted from workshop presentations and subsequent discussion are presented. Six papers published as part of this special issue of Ecological Engineering, and summarized here, deal with the general principles of mineland restoration, acidification effects and mitigation in Poland, reestablishment of riparian buffer strips in Estonia, recovery of forests in the Black Triangle of Czechoslovakia and Poland, restoration after 10 years near the Chernobyl nuclear plant accident in the Ukraine, and studies on remediation of contaminated soils in Belarus.     

红树林湿地在海岸生态系统维护中的功能*

综述了红树林湿地在海岸生态系统中所具有的维护生物多样性、防风消浪、促淤护岸、防灾减灾、净化海水、调节大气和美化海岸带景观等方面的功能。探讨了广东及华南沿海红树林的分布状况和存在问题,指出了华南沿海现存的红树林湿地正在遭受严重的威胁和破坏。华南沿海现存红树林湿地面积仅有1.5×10⁵hm²,比历史最大面积减少了70%;广东省的红树林湿地由10年前的1.47×10⁴hm²减少到现在的9100hm²,减少了38%。提出了建立和完善红树林自然保护网络系统、积极实施红树林湿地生态修复工程、注重红树林的引种和种苗培育技术研究、充分评估红树林湿地的巨大生态效价等对策与建议。     

How ecological engineering can serve in coastal protection

Traditionally, protection of the coastal area from flooding is approached from an engineering perspective. This approach has often resulted in negative or unforeseen impacts on local ecology and is even known to impact surrounding ecosystems on larger scales. In this paper, the utilization of ecosystem engineering species for achieving civil-engineering objectives or the facilitation of multiple use of limited space in coastal protection is focused upon, either by using ecosystem engineering species that trap sediment and damp waves (oyster beds, mussel beds, willow floodplains and marram grass), or by adjusting hard substrates to enhance ecological functioning. Translating desired coastal protection functionality into designs that make use of the capability of appropriate ecosystem engineering species is, however, hampered by lack of a generic framework to decide which ecosystem engineering species or what type of hard-substrate adaptations may be used where and when. In this paper we review successful implementation of ecosystem engineering species in coastal protection for a sandy shore and propose a framework to select the appropriate measures based on the spatial and temporal scale of coastal protection, resulting in a dynamic interaction between engineering and ecology. Modeling and monitoring the bio-physical interactions is needed, as it allows to upscale successful implementations and predict otherwise unforeseen impacts.     

Experimental wet heath translocation in Dorset, England

Heathland has become fragmented throughout its European range with many countries losing 60-90% of their heathland area during the 20th century. A small, isolated area of wet heathland within permitted ball clay workings in Dorset (England) was translocated in October 1993 to an engineered receptor cell fed by groundwater and direct precipitation in order to mitigate the otherwise total loss of the wet heath. The aims were to rescue the wet heathland and to re-establish a community type similar to the wet heath that originally occurred at the donor site prior to the recent development of vegetation communities and birch colonisation associated with drier conditions. Vegetation monitoring over 12 years up to 2005 indicated that the experimental translocation successfully fulfilled the aims for a period of 7 years when the hydrological regime of the receptor site was actively managed. There was development of a mosaic of wet heath and mire vegetation community types including Sphagnum lawns and open bog pools. However, when active management ceased, the receptor site became drier and species were lost. Multivariate analysis revealed a trajectory of progressive rapid chronological change during 1994 and 1995 followed by a period of relative stability between 1996 and 2000 which coincided with greater species density. Subsequently up to 2005, the plant community became less species-rich and the plant community reverted to a species structure similar to that which occurred in 1994/1995. The importance of hydrological regime for plant community structure was tested using fixed-quadrat data and the water level measurements made in the period 1995-1998. Canonical Correspondence Analysis (CCA) multivariate analysis revealed a hydrological gradient with a significant seasonal effect of water table depth in the first half of the year and close association of the least wet quadrat location and non-mire species. Overall, the results support the use of translocation as a means of rescuing wet heath habitat which would otherwise be lost due to change in land use. There is a risk of failure when translocating a complex ecosystem such as wet heath but ecological engineering provides an insight into defining the risk. Our results demonstrated that an ecologically acceptable outcome for a wet heath translocation can be achieved with careful design and implementation and sensitive management of the receptor site. However, it is essential to secure long-term hydrological and vegetation management in order to provide a sustainable outcome for long-term survival of a target wet heath community.     

The Sustainable Process Index a new dimension in ecological evaluation

The Sustainable Process Index (SPI) is a measure developed to evaluate the viability of processes under sustainable economic conditions. Its advantages are its universal applicability, its scientific basis, the possibility of adoption in process analyses and syntheses, the high sensitivity for sustainable qualities, and the capability of aggregation to one measure. It has proved to be useful in industrial strategic planning. The concept of the SPI is based on the assumption that in a truly sustainable society the basis of economy is the sustainable flow of solar exergy. The conversion of the solar exergy to services needs area. Thus, area becomes the limiting factor of a sustainable economy. The SPI evaluates the areas needed to provide the raw materials and energy demands and to accommodate by-product flows from a process in a sustainable way. It relates these areas to the area available to a citizen in a given geographical (from regional to global) context. The data necessary to calculate the SPI are usually known at an early stage in process development. The result of the computation is the ratio between the area needed to supply a citizen with a given service and the area needed to supply a citizen with all possible services. Thus, it is a measure of the expense of this service in an economy oriented towards sustainability.     

关于生态场的几点评述

依据植物生态场的系统研究资料,对生态场的概念、场和特征函数、生态场折图形以及生态场对植物相互作用的解释进行了评述。阐明了生态场的最基本属性是物质性,目前的研究水平尚不能确定生态场是还是有别于一稻物理场的特殊形式在场,对生态场的基本特征函数－生态热模型给予了形式与模型参数体测方面的评述,表明两种生态势模型各有一定的特点与优越性。作者强调,生态场更具生态学的方法论意义,应用生态场对植物相互作用形式与过