10.08.2026

Renaturation: Definition, Function, Benefits, and Examples

Building design

Snow-covered riverbanks in winter—a serene scene from nature during the cold season. (Photo: sagatto / Unsplash)

Rivers that are allowed to meander once again. Marshes that can breathe again. Floodplains that are flooded once more. Renaturation means far more than simply undoing human interventions in nature: It is one of the most powerful strategies available to landscape architecture, urban planning, and ecology combined to transform degraded ecosystems back into functional habitats, promote biodiversity, mitigate the effects of climate change, and improve the quality of life in both urban and rural areas. Those who understand renaturation understand how planning not only shapes the landscape but also heals it.

What Renaturation Means: Definition, Scope, and Technical Terms
Historical Background: Why Landscapes Became Degraded in the First Place
Ecological functions and ecosystem services of renaturalized areas
Renaturation as a Tool for Climate Protection and Climate Adaptation
Typical Renaturation Measures: Watercourses, Bogs, Floodplains, Urban Landscapes
Planning Law Fundamentals and Integration into Specialized Legislation and Funding Programs
Common Mistakes, Misconceptions, and Limitations of Renaturation
Renaturation in an Urban Context: Opportunities for Open Space Planning and Urban Development

Significance of Renaturation: Definition, Delimitation, and Technical Terms

Renaturation refers to the targeted restoration of natural or near-natural conditions in ecosystems whose structure, function, and biodiversity have been impaired by human use, technical interventions, or overuse. The term is derived from the Latin “natura” and essentially means returning an area or body of water to a state that once again allows ecological processes to take place. In technical terminology, renaturation is often used synonymously with the English term “ecological restoration,” although the latter is somewhat broader in international discourse and also includes measures in less severely disturbed systems.

The concept of renaturation must be distinguished from related concepts that are often conflated in planning practice. Recultivation refers to the restoration of agricultural or forestry usability, not necessarily to an ecological state. Revitalization refers to the revitalization of an area, often with a stronger focus on the quality of use for people. From a nature conservation perspective, the term “restoration” is more precise, as it aims to restore a historically defined reference state. The Society for Ecological Restoration (SER) defines “ecological restoration” as the process of supporting the recovery of an ecosystem that has been impaired by degradation, damage, or destruction. This definition makes it clear that renaturation is not a one-time act, but rather a process that requires initiation, support, and monitoring.

In German planning practice, renaturation is used as an umbrella term for a broad spectrum of measures: extending the course of straightened streams, re-wetting drained wetlands, removing bank reinforcements along rivers, reversing drainage in wet meadows, unsealing paved areas in cities, or creating wildflower strips on intensively farmed land. These measures differ considerably in terms of the extent of intervention, time required, and scope of impact, but they share the common goal of enabling ecological processes that have been interrupted or prevented by human use.

Historical Background: How Landscapes Were Degraded

The significance of renaturation can only be fully grasped by understanding the processes that led to the degradation of ecosystems. In Central Europe, the causes are deeply rooted in the history of agriculture, industry, and settlement. The systematic straightening of watercourses began on a large scale in the 18th and 19th centuries, when engineers forced rivers and streams into dead-straight channels for navigation, drainage, and flood control. In the process, the Rhine lost large sections of its natural meanders and floodplains; the same is true for the Elbe, Oder, Isar, and countless smaller waterways. The result was a dramatic loss of habitat for fish, amphibians, insects, and birds, as well as an accelerated discharge of floodwaters, which led to increased damage downstream.

Over the centuries, wetlands were drained and converted into agricultural land. In Germany alone, it is estimated that more than ninety percent of the original wetland areas have been destroyed or severely degraded by drainage, peat extraction, or land conversion. This has resulted not only in the loss of habitats for highly specialized species but also in the loss of enormous carbon sinks: Intact peatlands sequester more carbon per unit area than any other terrestrial ecosystem type. Their drainage releases this carbon as CO₂ and methane, turning degraded bogs into significant sources of greenhouse gases.

In cities, degradation occurred through soil sealing, the channeling of streams, and the alteration of natural terrain structures. Many urban streams were diverted into underground pipes in the 20th century to create building land or reduce flood risks. The result was ecologically dead channels beneath the city, while above ground, all connections to the natural water cycle were severed. This history of transformation serves as the starting point from which restoration measures are now taking effect.

Ecological Functions and Ecosystem Services of Renaturalized Areas

The ecological significance of renaturation lies in the restoration of ecosystem functions, which experts today describe as ecosystem services. This term encompasses all the benefits that natural systems provide to people and society, ranging from drinking water filtration and the pollination of crops to the regulation of the local climate. Renaturalized areas provide these services to an extent that technical alternatives rarely achieve—and when they do, it is only at a fraction of the cost.

Renaturalized watercourses with restored meanders, gravel banks, and riparian woodlands provide spawning habitats for fish, habitats for dragonflies, kingfishers, and dippers, filter nutrients from the water, and slow the flow during floods. The slowing of runoff is one of the most important services: A meandering stream has a significantly longer flow path than a straightened channel of the same length, which increases the water’s retention time and attenuates flood peaks. This natural retention effect is recognized in water management as decentralized flood protection and is systematically utilized in modern watercourse development concepts.

Restored wetlands provide ecosystem services on multiple levels simultaneously. As carbon sinks, they sequester organic material over millennia, as long as they remain water-saturated. As water retention systems, they buffer precipitation events and slowly release water during dry periods. As habitats, they are home to highly specialized species communities, including many endangered plant and animal species that have no chance of survival outside of bogs. The importance of restoration for climate protection is particularly high in the case of bogs: Every hectare of rewetted raised bog reduces annual greenhouse gas emissions by several metric tons of CO2 equivalents.

Restored floodplains—that is, the flood zones along rivers that are once again allowed to flood periodically—develop extraordinary biodiversity. The dynamics of flooding, drought, sediment deposition, and pioneer vegetation create a diversity of microhabitats that static landscapes cannot provide. Softwood floodplains with willows and poplars, hardwood floodplains with oaks and ash trees, reed beds, gravel banks, and oxbow lakes are components of a mosaic that ranks among the most species-rich habitats in Central Europe.

Renaturation as a Climate Protection and Climate Adaptation Strategy

The importance of restoration for climate protection has moved to the forefront of technical and political discourse in recent years. At the European level, the EU Nature Restoration Law—which was adopted following intense political debate—has established binding targets for the restoration of degraded ecosystems in the member states. It requires member states to restore at least twenty percent of the EU’s land and marine areas by 2030 and to bring all ecosystems in need of restoration to a good condition by 2050. These targets are ambitious and require a significant expansion of planning capacities and funding.

Climate adaptation and climate protection are not separate goals in restoration; rather, they are intertwined. Restored areas cool their surroundings through evaporation, provide shade for water bodies and soils, store water in the ground rather than allowing it to drain away quickly, and thus reduce the heating of urban and rural areas. Particularly in cities, where heat island effects are especially pronounced due to soil sealing and high building density, the restoration of brownfields, urban streams, and green corridors can make a measurable contribution to temperature regulation. In this context, experts refer to “green” and “blue-green” infrastructure—that is, interconnected systems of vegetation and water that are understood as functional elements of urban planning.

The connection between renaturation and the water cycle is particularly relevant in times of increasing droughts. Renatured soils with a high organic content and an undisturbed soil structure absorb stormwater more quickly, store it longer, and release it more evenly than compacted or impervious soils. This “sponge effect,” which experts refer to as on-site water retention, is one of the most effective responses to the increasing frequency of extreme weather events that alternate between heavy rainfall and drought.

Typical restoration measures: watercourses, wetlands, floodplains, and urban landscapes

The range of specific restoration measures is broad, and their selection depends on the initial condition of the ecosystem, the planning objectives, and the available resources. For watercourses, the spectrum includes extending the course by restoring meanders, removing riverbed sills and transverse structures, removing concrete or rock-fill bank reinforcements, establishing riparian forest strips, and reconnecting oxbow lakes. Each of these measures has varying degrees of effectiveness and different requirements in terms of area, time, and level of intervention.

In peatland restoration, the focus is on rewetting. Drainage ditches are filled in or sealed with dams made of peat or wood to raise the water level. This process is not reversible in the sense that a bog immediately returns to its original state: the re-colonization by bog-typical vegetation, particularly peat mosses (Sphagnum), can take decades. Nevertheless, the reduction in greenhouse gas emissions begins shortly after rewetting, because the decomposition of organic material is greatly slowed when the peat is water-saturated.

In an urban context, stream restoration is one of the most visible and effective forms of renaturation. Urban streams that were piped in the 20th century are brought back into the open, embedded in near-natural channels, and lined with riparian vegetation. Well-known examples from German-speaking countries show that such projects not only have ecological benefits but also significantly improve the quality of life in urban neighborhoods and serve as places where residents can feel a sense of belonging. The combination of ecological function and social quality makes stream restoration a prime example of multifunctional open-space planning.

De-sealing and Land Renaturation in Urban Areas

Unsealing—that is, the removal of asphalt, concrete, or other impermeable surfaces and the restoration of living soil—is a form of restoration that holds particular significance in an urban context. Every square meter of unsealed area improves the soil’s infiltration capacity, reduces surface runoff during heavy rainfall, and creates potential for vegetation. However, unsealing alone does not constitute restoration in the full sense: Unsealed soil that is subsequently compacted or planted with vegetation unsuited to the site will realize only a fraction of its potential ecological performance. The key lies in restoring a functional soil ecosystem that supports soil structure, water balance, and nutrient cycling.

Brownfield sites in cities—whether former industrial areas, abandoned rail yards, or residual plots within the urban fabric—often harbor a surprisingly high level of biodiversity because pioneer vegetation and succession communities develop there without human intervention. Planning practice faces the question of how much intervention is appropriate: complete renaturation with active planting, guided succession with targeted interventions, or leaving the area open with monitoring. The answer depends on the planning objectives, the timeframe, and the location within the urban fabric.

Planning Law Foundations and Integration into Specialized Legislation

In Germany, renaturation is embedded in a dense network of sector-specific laws, planning instruments, and funding programs. The Federal Nature Conservation Act (BNatSchG) obligates the federal and state governments to safeguard and restore biological diversity and the functionality of natural ecosystems. The Impact Regulation, a central instrument of German nature conservation law, requires that unavoidable impacts on nature and the landscape be offset by compensatory and replacement measures. Renaturation measures are frequently planned and implemented as such compensatory measures, which gives them an important role in day-to-day planning.

The EU Water Framework Directive (WFD) requires member states to achieve good ecological status for all surface waters. This goal cannot be achieved without renaturation measures on watercourses, which is why the WFD has provided a strong impetus for watercourse renaturation throughout Europe. In Germany, the federal states implement these requirements through management plans and programs of measures that identify and prioritize specific renaturation projects. Funding is provided through EU funds (EAFRD, ERDF), federal programs, and state funds, although the funding landscape is complex and often difficult for planning firms and municipalities to navigate.

The integration of restoration goals into land-use planning is also relevant for open-space planning. Land-use plans can designate areas for measures to protect, maintain, and develop nature and the landscape; zoning plans can establish corresponding provisions. Landscape plans and green space plans are the specialized planning tools used to give renaturation goals concrete spatial form and to incorporate them into the balancing of competing land-use claims.

Common Mistakes, Misconceptions, and Limitations of Renaturation

A common misconception is to view renaturation as simply reverting to a previous state. In fact, the reference state to which renaturation refers no longer exists or is no longer attainable in most cases. Soils, groundwater levels, species compositions, and hydrological conditions have changed so much over decades or centuries of use that a complete restoration to the historical state is neither possible nor practical. Renaturation therefore realistically aims for a functional, near-natural state, not a historical reconstruction.

Another mistake in planning practice is underestimating the time required. Ecosystems do not develop according to human project timelines. A restored stream takes years for a stable stream morphology to establish itself; a rewetted bog takes decades for peat mosses to become dominant; a restored forest takes generations. Renaturation projects that are considered complete after three years of monitoring often capture only the initial phase of a long-term development. Long-term monitoring and adaptive management strategies—that is, the willingness to respond to unexpected developments and adjust measures accordingly—are therefore indispensable components of any serious renaturation concept.

Renaturation can also fail if the conditions in the watershed are not right. A renatured stream that continues to receive high nutrient inputs from agriculture will not develop a near-natural aquatic biocoenosis, no matter how effective the measures along the watercourse itself may be. Renaturation must therefore be approached systemically: Measures along the watercourse, in the floodplain, and within the watershed must be coordinated. Isolated, individual measures that do not take the landscape level into account will have limited effectiveness.

Renaturation as a Future Task for Landscape Architecture

Renaturation only fully realizes its significance when it is understood as an integral task of landscape architecture and open-space planning, rather than as a niche topic of nature conservation. The challenges of climate change, biodiversity loss, and resource scarcity make the restoration of ecological functions a core task of planning in the 21st century. Landscape architects, urban planners, and open-space planners are called upon to integrate renaturation goals into all levels of planning, from regional planning down to the detailed design of a city square.

The combination of ecological function and design quality is not a limitation but an opportunity. Renaturalized areas that are experienced as attractive open spaces enjoy broader social acceptance and are protected more sustainably than areas perceived solely as ecological compensation areas. The design of transitions, pathways, viewpoints, and recreational areas along renaturalized waterways or wetlands is a core task of landscape architecture that combines ecological effectiveness with quality of use.

The significance of renaturation for society will grow as the consequences of the loss of ecological functions become increasingly apparent: through flooding, heat waves, drinking water shortages, and the decline of pollinators. Anyone who views restoration as an investment in functioning landscapes that provide services no technology can fully replace has grasped the core argument for this planning task. This is not about sentimentality toward a lost natural world, but rather the sober realization that intact ecosystems are the foundation for resilient cities and regions.

31.08.2026

Translated: Wissenswertes

Large Landscape Gardens: Fundamentals, History, and Significance

Building design

A landscaped garden and park complex designed around the theme of the Grand Landscape Garden — A street with flowers planted along a concrete wall—an example of urban greening. Photo: rumanamin/Unsplash

Anyone who enters a large landscape garden experiences nature as a work of art: vast lawns that gently give way to groups of trees, winding paths that continually draw the eye in new directions, bodies of water that reflect the sky, and sightlines that stretch across hills and valleys. The large landscape garden is one of the most influential inventions in European garden design—a design philosophy that, since the 18th century, has fundamentally redefined the relationship between people, nature, and space, and continues to shape open-space planning to this day.

What defines a grand landscape garden and how it differs from other types of gardens
How the landscape garden emerged historically and which intellectual movements shaped it
Which design principles and design elements underlie the landscape garden
What plant selection and vegetation techniques are characteristic of large-scale landscape gardens
How care, maintenance, and historic preservation are organized for historic landscapes
The significance of the landscape garden for contemporary urban development and open-space planning
What common misunderstandings and mistakes occur in planning and maintenance
How large-scale landscape gardens are being reevaluated in the context of climate adaptation and biodiversity

Definition and Classification: What Is a Large Landscape Garden?

The large landscape garden, known in English-speaking countries as a “landscape garden” or “English landscape garden,” is a type of open space that deliberately eschews the formal, geometric garden design of the Baroque and Renaissance periods and instead takes an idealized natural landscape as its design basis. It is characterized by meandering paths and shorelines, freely shaped bodies of water, irregularly arranged groups of trees and shrubs, expansive lawns, and a carefully staged sequence of spatial impressions. The word “large” refers not only to the area—which in fact often spans several hundred to over a thousand hectares—but also to the conceptual aspiration: the garden as a reflection of a complete, internally coherent landscape.

The large landscape garden differs fundamentally from the Baroque palace garden in its design logic. While the Baroque garden controls and organizes nature through symmetry, axes, parterres, and topiary (the pruning of trees and shrubs into geometric shapes), the landscape garden simulates the random, the organic, and the picturesque. This simulation, however, is by no means random: It is based on precise design decisions and the deliberate use of topography, vegetation, water, and architecture to create specific moods, visual relationships, and spatial experiences. In this sense, the landscape garden is a highly refined art form that conceals its methods.

Typologically, the large landscape garden can be distinguished from smaller landscape-style home gardens, 19th-century public parks, and modern city parks, even though all these types have emerged from it or been influenced by it. The decisive difference lies in scale and intention: the large landscape garden is a total work of art that reinvents an entire landscape, whereas the 19th-century city park primarily served social and hygienic purposes, and the landscape-style private garden merely borrows formal elements.

Historical Origins: England, the Enlightenment, and Criticism of the Baroque

The roots of the grand landscape garden lie in early 18th-century England, where a combination of philosophical, literary, and political currents gave rise to a new aesthetic of nature. The Enlightenment, with its trust in reason and the observation of nature, stood in productive tension with the contemporary longing for the sublime and the picturesque—that is, for landscapes that evoke awe, vastness, and irregularity. Poets such as Alexander Pope, philosophers such as Anthony Ashley Cooper, the third Earl of Shaftesbury, and painters such as Claude Lorrain and Nicolas Poussin—whose landscape paintings served as direct models—shaped the aesthetic program of the new garden style.

The gardens at Stowe (Buckinghamshire), Stourhead (Wiltshire), and Rousham (Oxfordshire) are considered key early examples. At Stowe, Charles Bridgeman, William Kent, and finally Lancelot “Capability” Brown—who would become the most influential landscape architect of the 18th century—worked in succession. Brown earned his nickname “Capability” from his habit of identifying the “capabilities” of a site for improvement. His style, characterized by meandering lakes, gently undulating lawns, clusters of trees, and belts of trees along the edges, became the epitome of the English landscape garden and influenced hundreds of gardens throughout Great Britain.

At the same time, a theoretical debate developed about the picturesque, led primarily by William Gilpin, Uvedale Price, and Richard Payne Knight. These authors criticized Brown’s style as too smooth and too orderly and called for a rougher, wilder garden aesthetic more closely aligned with painting. This debate is important for understanding the grand landscape garden because it shows that the style was not a uniform doctrine but a dynamic field of aesthetic debate.

The landscape garden style reached Germany in the second half of the 18th century, initially through travelogues and publications, then through direct commissions of English gardeners and the work of local designers such as Friedrich Ludwig von Sckell, who laid out the English Garden in Munich, and Peter Joseph Lenné, who had a decisive influence on the Potsdam park landscape surrounding the New Garden and Sanssouci Park. Prince Franz von Anhalt-Dessau created the Wörlitz Park, the first significant landscape garden project on German soil, which is now a UNESCO World Heritage Site. In these German gardens, the English landscape style is often combined with Enlightenment-era educational programs: temples, inscriptions, monuments, and symbolic structures transform the garden into a walk-through total work of art with a moral and political message.

Design Principles and Design Elements of the Grand Landscape Garden

The grand landscape garden employs a range of design elements that, when combined, create its characteristic spatial experience. The most important element is the staging of visual relationships: the path through the garden is a sequence of images that the designer has deliberately composed. Axial views open up onto temples, bridges, or bodies of water; groups of trees and shrubs frame vistas and block unwanted views; hills and depressions create moments of surprise when, after an ascent, a sweeping view suddenly opens up.

Water plays a central role. Natural or artificially created lakes and ponds with irregular, curved shores are a hallmark of the style. Capability Brown was famous for transforming rivers into expansive lakes through damming, which gave the impression of natural bodies of water. The reflection of the sky and the surrounding vegetation on the water’s surface significantly enhances the sense of depth in the space. Bridges, islands, and shoreline plantings complement the body of water as design elements.

Vegetation is conceived not as individual plants but as mass and volume. Solitary trees—that is, freestanding individual trees with distinctive shapes or sizes—provide focal points within the lawn. Groups of trees and shrubs of varying sizes and compositions structure the space and create a layering of foreground, middle ground, and background reminiscent of landscape painting. Belts of trees and shrubs along the garden’s edges enclose the grounds from the outside and create the impression of a self-contained world. The lawn itself, referred to in the original English as “lawn,” is not merely leftover space but a design element: it connects the groups of trees and shrubs, guides the eye, and gives the garden its sense of expansiveness.

Architectural features—such as temples, grottoes, ruins, bridges, obelisks, and similar structures—complete the picture. They are not functional buildings but rather convey meaning: they allude to ancient models, literary themes, or the client’s worldview. Ruins, whether genuine or artificially created, are a particularly characteristic element because they symbolize transience and the superiority of nature over human creation—a central theme of Enlightenment aesthetics.

Plant Selection and Vegetation Design in the Landscape Garden

The use of plants in large landscape gardens follows different principles than in formal gardens. The focus is not on the individual plant with its botanical characteristics, but on the effect of the mass of plants within the space. For woody plantings, native tree species were and continue to be used predominantly; in Central Europe, these include oak, beech, hornbeam, linden, ash, maple, and alder, supplemented by introduced species such as plane tree, horse chestnut, and various conifers, which have been widespread in European landscape gardens since the 18th century.

Creating woody plantings in the landscape garden style requires thinking in terms of long time frames. A tree planted today as a solitary specimen will not fully unfold its spatial impact until decades later. Capability Brown is said to have remarked that he worked for posterity, not for the present. This temporal dimension is a fundamental difference from architecture: the landscape garden is never finished; it changes continuously through the growth, aging, and loss of trees and shrubs. Professional care and maintenance must guide this process without destroying the original design concept.

The lawns of historic landscape gardens were originally maintained through grazing by sheep and cattle, which also served an ecologically valuable purpose. With the invention of the lawn mower in the 19th century and the increasing mechanization of maintenance, maintenance practices changed fundamentally. Today, those responsible for maintenance face the challenge of balancing the preservation of the historic character, the demands of visitor use, and the goals of promoting biodiversity. Extensive meadow management with infrequent mowing, the creation of wildflower strips, and the promotion of old-growth wood in groups of trees and shrubs are strategies that are increasingly being incorporated into modern maintenance concepts for historic landscape gardens.

The introduction of exotic woody plants, particularly rhododendron species and conifers from North America and East Asia, was a significant expansion of the plant repertoire in the 19th century. Many historic landscape gardens today contain significant collections of these species, which have since acquired historical value in their own right. At the same time, Rhododendron ponticum has become an invasive problem in Atlantic-influenced regions of Great Britain and Ireland, threatening the ecological integrity of historic sites. This tension between historical authenticity and ecological responsibility is a central theme in today’s preservation of landscape gardens.

Maintenance, Preservation, and Management Concepts for Historic Sites

Historic landscape gardens pose special challenges for heritage conservation because their heritage value lies not in solid materials but in a living, ever-changing composition of vegetation, topography, water, and architecture. The challenge lies in preserving the spirit of the original design without freezing the growth of the vegetation or reducing the site to an artificial state. Maintenance concepts for historic landscape gardens must therefore be based on a careful historical analysis that evaluates sources such as original plans, paintings, engravings, travelogues, and plant lists.

In Germany, historic garden conservation has established itself as a distinct discipline situated at the intersection of landscape architecture, historic preservation, and garden history. The Florence Charter, a document adopted in 1981 by the International Council on Monuments and Sites (ICOMOS), defines principles for the preservation of historic gardens and parks. It emphasizes that the historic garden is a living monument that requires continuous care, and that restoration measures must be based on documented sources.

Practical maintenance tasks in historic landscape gardens include the regular inspection and care of tree and shrub populations, the preservation and restoration of water features and ornamental structures, the maintenance of lawns and paths, and the management of visitor flows. The latter is a particularly complex task in heavily visited sites such as the English Garden in Munich or Sanssouci Park in Potsdam, where user needs, historic preservation, and ecological goals must be balanced. Foot traffic, soil compaction, and damage to the root systems of old trees caused by visitors are real threats that are mitigated through route guidance, signage, and, if necessary, temporary closures.

Significance for Contemporary Open-Space Planning, Climate Adaptation, and Biodiversity

The large landscape garden is not a museum relic, but rather a reference model that remains highly relevant for today’s open-space planning and urban development. Its fundamental principles—the linking of open spaces into contiguous green spaces, the use of topography and water as design elements, and the creation of spatial diversity through the alternation of open and enclosed areas—are reflected in modern concepts such as the Green Belt, Green Infrastructure, and the 21st-century city park.

In the context of climate adaptation, this type of landscape garden offers specific advantages. Extensive stands of trees and shrubs create cooling effects through evaporation and shading, which are increasingly in demand in overheated cities. Extensive lawns and water bodies help regulate the urban water cycle by absorbing, temporarily storing, and gradually releasing rainwater. The topography of many historic landscape gardens—with hollows, depressions, and ponds—corresponds in its basic structure to the principle of the “sponge city” (a concept of water-sensitive urban planning), which is currently being discussed as a response to increasing heavy rainfall events.

For biodiversity, large-scale landscape gardens—with their stands of mature trees, extensive lawns, bodies of water, and wooded edges—serve as valuable habitats. Old oaks, beeches, and linden trees, with their hollows, cracks, and dead branches, provide habitat structures for bats, woodpeckers, beetles, and numerous other species that can hardly find a place in intensively used urban landscapes. Promoting deadwood, adopting a more extensive approach to lawn care, and creating riparian buffer zones are measures that can enhance the ecological value of historic landscape gardens without compromising their character.

At the same time, open-space planning must critically reflect on what the grand landscape garden historically also was: an instrument of land acquisition and social segregation. Many of the most significant English landscape gardens were created through the enclosure and transformation of common land—a process that displaced villages and dispossessed farmers. This socio-historical dimension is essential to a complete understanding of the type, even if it does not negate its aesthetic and ecological value.

The Grand Landscape Garden as an Enduring Design Model

The large landscape garden established a design philosophy that extends far beyond its historical context of origin. The idea that open space is designed not through geometry but through reflection on spatial sequences, visual relationships, movement, and atmosphere remains a fundamental principle of landscape architecture to this day. Anyone planning a city park, a park complex, or a large-scale open space works—consciously or unconsciously—with techniques developed in 18th-century English landscape gardens.

The strength of this typology lies in its adaptability. The large landscape garden can serve simultaneously as a recreational space, a nature conservation area, a climate buffer, a cultural heritage site, and a source of urban identity. It requires its planners and caretakers to think in the long term, to understand ecological processes, and to exercise aesthetic judgment that transcends short-term trends. This combination makes it a challenging yet rewarding field of practice for landscape architecture.

The great historic gardens—from Stourhead to Wörlitz to the English Garden in Munich—are not only testaments to a bygone era of garden art, but also living laboratories where one can observe how vegetation, topography, water, and architecture have interacted over the centuries. Anyone who walks through these gardens with a knowledgeable eye learns more about open-space planning than from many textbooks. The grand landscape garden remains what it has been since its inception: a design model of extraordinary depth and durability.

03.12.2024

Industry news, Trick

Listen to this Podcast

Building design

Museums are not the only ones using podcasts to introduce themselves. Conservation science is also discovering this medium. Students at the University of Amsterdam have now launched a conservation podcast The new podcast format “ECPodcast – by and for Emerging Conservation Professionals”, which five Master’s students at the University of Amsterdam have developed in recent weeks, is just over two weeks old. The series […]

Museums are not the only ones using podcasts to introduce themselves. The restoration sciences are also discovering this medium. Students at the University of Amsterdam have now launched a restoration podcast

Students at the University of Amsterdam have now launched a restoration podcast
Photo: Screenshot Instagram/ecpodcast

The new podcast format “ECPodcast – by and for Emerging Conservation Professionals”, which five Master’s students at the University of Amsterdam have developed in recent weeks, is just over two weeks old. The series provides insights into the “Conservation & Restoration” course at the University of Amsterdam. In the first episode, Mané van Veldhuizen, Anthi Soulioti, Willemijn Bolderman, Terri Costello and Liz Hébert talk about their specializations and report on their recruitment test. They have now been at university for a year. The second episode is already online – here the students talk to Professor Ellen Hendriks, who is involved in the program’s application process: How did Covid-19 affect the selection week? Just listen in: www.ecpodcast.de