SUSTAINABLE? GOLF
Golfing for Change
Case study Lunds Akademiska Golfklubb
Site Kungsmarken
Year 2026

SUSTAINABLE? GOLFING

Golf courses are typically seen as antithetical to sustainability. This project takes a more nuanced stance: it depends on place, time and practices. We collaborated with Lunds Akademiska Golfklubb to explore how ninety hectares of protected reserve are kept for play, for orchids, and for everyone.

Scroll, or use the navigation above to move between the report, the photo narrative, and the people behind the work.
Lund · Skåne · Sweden
Photo · Course at dusk
Land
90 ha
Total course area inside the Natura 2000 reserve.
Water
1.5 ha
Of irrigated turf — the greens only. The other 88.5 ha are unwatered.
Biodiversity
400+species
Documented on the course since it was established in 1936, including ten orchid species.
Chemistry
0herbicides
Pesticide and fertiliser use is restricted to the greens. No herbicide anywhere on site.
§ 01 · The project

A communication concept, grounded in evidence.

Lund University · 2026

Lunds Akademiska Golfklubb already manages its course more sustainably than the industry norm. The gap that remains is not in practice — it is in how that practice is seen, by golfers and by the wider public.

Working with LAGK, we built a communication concept of signs, posters, a photo exhibition, and this site — each one anchored in our own biodiversity and surface-runoff analysis. The goal is not to advertise. It is to make a statement: Sustainable management exists and should be visible enough to become an expectation.

§ 02 · The data

The data, made visible.

Six findings drawn from the field assessment, the Artportalen record, and modelling — biodiversity, chemical use, water consumption, and climate-driven flood risk.

Fig. 01

Density of Endangered Species

Kernel density map of endangered species across Kungsmarken
LAGK is home to a range of endangered species. Areas with the highest density are shown in darker colour — the densest concentration is right in front of you. Please do not enter it, so the orchids can thrive.
Fig. 02

Flora through time

Bloom windows across seven orchid species. Each shape is a symmetric distribution — start and end at the species' flowering boundaries, peak near mid-bloom.

The ten orchid species at Kungsmarken bloom in a staggered sequence from late April through July — Cuckoo keys open first, Lesser butterfly-orchid closes the season. The overlap is deliberate: the wider the bloom window, the longer the pollinator larder. Mowing the rough on a single late-summer pass is what makes this calendar possible.

Fig. 03

Chemical Use Compared

LAGK Average Swedish Golf Club Swedish Agriculture
Kilograms of fertiliser per hectare per year
LAGK
2.97 kg
Avg. golf
16.96 kg
Agriculture
93.5 kg
Kilograms of pesticide per hectare per year
LAGK
0.05 kg
Avg. golf
0.18 kg
Agriculture
1.11 kg
Annual fertiliser and pesticide load per hectare. LAGK restricts both to the greens only — 1.5 ha out of 90.

The per-hectare figure flatters LAGK in one direction and understates the difference in another. The club only treats the 1.5 ha of greens — the remaining 88.5 ha receive nothing. Compared on total site load, LAGK's annual chemistry footprint is roughly a sixtieth of an average Swedish course of the same size, and a fortieth of an equivalent arable hectare.

Fig. 04

Water Use Compared

Cubic metres of water used per year
Avg. North Swedish golf club
8 200 m³
LAGK
11 000 m³
100 Swedish households
11 400 m³
Avg. Swedish golf club
32 500 m³
Avg. Swedish farm
33 000 m³
Avg. North US golf club
52 000 m³
Avg. North France golf club
90 000 m³
Avg. South France golf club
175 000 m³
Avg. South US golf club
566 000 m³
Avg. Mediterranean golf club
625 000 m³
LAGK draws water from the on-site lake Glomsjön only for the greens and tees — comparable to 100 households, and roughly a third of an average Swedish golf course or farm.
Fig. 05

Flood threshold exceedance under climate scenarios

Today (baseline) 2060 — low estimate 2060 — high estimate
0 20 40 60 80 mm / hr 0.1 1 10 100 Return period (years) 5 mm/hr · localized flooding 7 mm/hr · concentrated flow 10 mm/hr · course closure 15 mm/hr · damage to orchids
1-hour rainfall intensity by return period, today and under 2060 low / high climate scenarios. The course-closure threshold (10 mm/hr) is crossed earlier and the orchid-damage threshold (15 mm/hr) sits within reach of routine storms under the high estimate.
Fig. 06

Events become this much more frequent by 2060

×1.5
5 mm/hr
every 3.1 mo → every 2.1 mo
Localized flooding
×1.7
7 mm/hr
every 4.5 mo → every 2.6 mo
Concentrated water flows
×2.2
10 mm/hr
every 8.0 mo → every 3.7 mo
Course closure
×3.1
15 mm/hr
1 in 1.7 y → every 6.5 mo
Damage to orchids
Frequency multiplier (2060 high vs today). The dashed line at ×1 is no change. The orchid-damage threshold becomes the most disproportionately frequent event, shifting from once every 1.7 years to roughly twice a year.
02 / 04

The Report

Method, findings, and the surprises — including a biodiversity hotspot map that contradicts the original reserve assessment.

Read the report
03 / 04

The Photo Story

Five scenes across the course, told in photographs and ambient sound. Scroll sideways through the orchards, the lake, and the fairway.

Enter the story
04 / 04

The People

Six students, four collaborators at LAGK, two agencies, one advisor, and one mentor whose framing the project both relies on and pushes against.

Meet the team
§ 02 · Report

The Report

Summary · key findings · one chart

A short version of the work: what we set out to ask, what the data said, and where it surprised us. The full paper sits behind this, but the headlines are here.

01
The framing

Public opinion on golf courses is divided. Critics point to the land they occupy, the water they consume, and the chemicals they release. Players see recreational space close to nature.

Both readings can be true on the same hectare of grass. The question is which reading is supported by what the course is actually doing — and whether anyone outside the club knows the answer.

The ecological value of golf courses depends on what habitats they replace. The alternative to a course is rarely untouched nature — it is residential development.
Ormiston & Cristol, 2025 — paraphrased
02
What we found

We combined verified observations from Artportalen with in-field assessment, surface-runoff modelling, and conversations with the club's management. The numbers below are the headlines.

98%
Of course area
Receives no irrigation. Water for the greens comes from the on-site lake Glomsjön, not the municipal supply.
10orchids
Orchid species
Including rare flora like the narrow-leaved lungwort. The hotspot near Green 12 is the densest concentration on the course.
6signs
Communication outputs
On-site signs at biodiversity hotspots, plus posters in the clubhouse, this site, and a physical photo exhibition.
03
The chart

Endangered flora observations across Kungsmarken, 1990–2026. Point size scales with the number of organisms; colour follows the IUCN Red List category. The cluster near Green 12 became the anchor for sign placement.

Fig. 1
Rare flora observations · Kungsmarken
Source · Artportalen
n = 312 verified records
1990 – 2026
GLOMSJÖN GREEN 12 · HOTSPOT N 200 M
CR · Critically endangered
EN · Endangered
VU · Vulnerable
NT · Near threatened
04
The surprise

The reserve's original habitat assessment singled out two grassland types as the priority for protection. Our observations don't agree.

The hotspots we see in the field — and the ones the Artportalen record confirms — sit in different places. The original framing has ossified around the assumptions of when the reserve was created. The lesson is methodological: authoritative framings have to be treated as data subject to revision, not as ground truth.

That discipline is the same one this project applies to its own framings, including the friendly one — that golf can be sustainable. It can. Sometimes. Where it is, the work of communicating it has barely started.

§ · The output

The signs

Three signs, anchored to the biodiversity hotspots. Each one points to a number that readers can verify against the data behind the report — biodiversity, chemical use, irrigation.

Scroll sideways
01 / 03
Sign · Biodiversity
01 / 03
Biodiversity

Posted at the meadow edge near Green 12 — the densest orchid cluster on the course.

Sign · Chemical Use
02 / 03
Chemical Use

Pesticide and fertiliser use is restricted to the greens. No herbicide anywhere on site.

Sign · Irrigation
03 / 03
Irrigation

Only the greens — 1.5 ha out of 90 — are watered, and from the on-site lake Glomsjön, not the municipal supply.

The full version
FULL REPORT

The long version. Abstract, problem framing, theoretical grounding, the modelling work, the communication concept, and the discussion that names where the project's design holds the line — and where it doesn't.

Course Knowledge to Action
Institution Lund University · 2026
Length ~ 25 min read
05
Abstract

Golf courses are typically seen as antithetical to sustainability due to their land, chemical, and resource usage. The aim of this project is to challenge that perception by emphasizing that golf can be sustainable, using Lunds Akademiska Golfklubb (LAGK) as a case study.

We address the integration of nature preservation and golf course use through the redesign of a hiking path, and through measures to improve the species richness of protected orchids. Through these interventions we aim to strengthen the club's existing sustainability profile and use it to demonstrate to the wider community that golf courses can prioritise environmental responsibility and serve purposes beyond recreation.

For current members, who already take pride in their course, this enhanced sustainability profile is intended to reinforce that pride and position improved environmental conditions as a shared value between the club and its members.

06
Problem description

Public opinion on golf courses is often divided. While they may be valued by golfers as recreational areas that are close to nature, they are also criticised for occupying large areas of land, restricting public access to nature, and having severe environmental impacts.

Briassoulis' (2011) analysis of global opposition against the expansion of golf-related tourism development shows that since the 1990s, local opposition against golf-related projects has at times been intense and, in some cases, even violent — particularly in developing countries and in the Mediterranean region. In Sweden specifically, golf has become an increasingly popular sport, while it is often argued that golf courses restrict public access to attractive land areas that could otherwise serve as recreational space. This issue is especially relevant in the Nordic context, where traditions of public access (allemansrätten) are strong (Sandberg et al., 2016).

Water

One of the most significant sustainability challenges golf clubs both create and face is the high water demand needed to maintain turfgrass. A study from Spain shows that golf courses compete with public water supply, agriculture, and business for freshwater resources in many countries (Rodríguez Díaz et al., 2011). In Sweden, golf courses are also active users of local water supplies (Bekken et al.). Gleeson et al. (2012) showed how many communities around the world have a groundwater footprint in which they use water at rates higher than the water can replenish, leading to the declining health of local surface-level nature.

In the future, Skåne will experience increased precipitation, increased extreme short-term precipitation, and higher air temperatures (Eklund et al., 2015). Latest CPM models predict precipitation increases of 1.36–1.68 for one-hour extremes by 2060 (An et al., 2025). These shifts will produce more floods and longer droughts, which is particularly acute for golf courses already experiencing periodic challenges with both — affecting user availability and on-course biodiversity.

The reason many golf courses have high water consumption is that they constantly pump water to replace evaporation in order to keep the grass green for aesthetics (Romero & Dukes, 2016). This usage is typically above what the local water table can sustain, sometimes leading to the use of recycled wastewater. While effluent water saves potable water, it leads to high salt buildup, which damages the soil and increases water demand to flush salts past the root zone (Leinauer et al., 2012). In periods of scarcity, golf courses often have usage restricted by municipalities (Salgot et al., 2012).

Chemicals and biodiversity

A second sustainability issue is intensive chemical use, which contributes to a third: biodiversity loss. Pesticides and fertilisers are used to maintain healthy turfgrass, both because high-quality turf is expected by users and because the grass must tolerate low-mowing and heavy traffic (Grégoire & Laliberté, 2025; Metcalfe et al., 2009). Intensive pesticide use to protect turf from insects, fungi, and weeds (Pathak et al., 2022) drives declining insect populations (Gebremariam, 2024), with ripple effects through food chains, pollination, and nutrient cycling.

Pesticides and excess nutrients from fertiliser can contaminate groundwater or be transported into adjacent watersheds by rainwater or irrigation, causing toxic impacts to aquatic organisms and triggering eutrophication (Bock & Easton, 2020; Metcalfe et al., 2009). The construction of golf courses also contributes to habitat fragmentation and loss of wildlife habitat by replacing complex ecosystems with simplified, highly managed landscapes (Fouillouze et al., 2023).

Metcalfe et al. (2009) argue that the key to lowering chemical impact is reduced use — and identify golfer education as the best management strategy, lowering cosmetic expectations so that less chemical use becomes acceptable to users. Keast's (2001) survey showed that most golfers enjoy encountering wildlife while playing and support increasing natural areas on courses; half also said they prefer a perfectly green playing area. The contradiction is the gap this project's communication concept aims to work in.

07
LAGK — a positive case

In this project, we have chosen to collaborate with Lunds Akademiska Golfklubb (LAGK). LAGK is located within Kungsmarken Nature Reserve, which is also a Natura 2000 site. The club, therefore, has to follow strict environmental regulations set by the Swedish government and the EU.

As a result, LAGK operates more sustainably than many other clubs across the three challenges named above. First, LAGK leaves large parts of the course non-irrigated: irrigation is limited to the greens, which cover only 1 hectare of the 90-hectare course. All irrigation water comes from lake Glomsjön on site, so LAGK does not compete with the local community for freshwater. Second, LAGK uses no herbicides; pesticides and fertilisers are applied only to the greens.

Third, while the construction of the course likely led to some biodiversity loss, that does not mean the course has reduced biodiversity in Kungsmarken over its lifespan. Ormiston & Cristol (2025) emphasise that the ecological value of golf courses depends on what habitats they replace.

Kungsmarken has a long history of human interference. In the Iron Age it hosted settlement and agriculture. During the Middle Ages, the Bishop of Lund built an estate here — Biskopsborgen Glomstorp. After that period, the area was used for grazing horses, and from 1918 to 1925 Kungsmarken served as a training ground for the Southern Scanian Infantry Regiment, which built a shooting range here. After the regiment's disbandment, voices were raised against various development proposals. According to LAGK's website, the construction of the golf course in 1936 saved Kungsmarken from invasive alternatives, such as the establishment of single-family farms.

Both naturalistic and conventional golf courses have higher species richness and abundance than residential areas — supporting the argument that the establishment of the course was better for the biodiversity of Kungsmarken than the alternative. Ormiston & Cristol, 2025 — paraphrased

Since its establishment, the club has contributed to the preservation of around 400 species in Kungsmarken, including ten orchid species, rare flora such as the narrow-leaved lungwort, and a rich bird life (LAGK, n.d.). Despite this — and the public emphasis on the reserve status — the outreach and communication regarding water management, habitat provision, and low chemical reliance have not yet been fully developed.

08
Project aim

The aim of the project is to raise awareness about the sustainability of the golf course at LAGK. The target audiences include both golfers and the general public who visit Kungsmarken — with LAGK serving as an ambassador for the broader concept of sustainable management practices on golf courses.

To achieve this, we developed a communication concept consisting of several complementary elements: place-specific physical signs around the course, posters, a website, and a physical photo exhibition. As part of the project we ran modelling analyses to examine water distribution across the course in combination with other parameters; the models informed the communication content and helped identify the best locations for signs, particularly near high-density biodiversity hotspots.

We designed three sign concepts and built six physical signs using these designs at the selected locations. The sign design highlights the positive initiatives undertaken by LAGK in water management and biodiversity conservation, while also communicating the broader sustainability challenges associated with golf courses in general. The three sign topics are: pesticide and fertiliser use, biodiversity conservation, and water use and irrigation. Posters using the same visual design were placed in the clubhouse and restaurant to reach visitors who come for the restaurant or driving range and may not encounter the on-course signs.

Both signs and posters include QR codes linked to LAGK's website. On the website we made five visual storytelling pieces that showcase the biodiversity of the course — focusing particularly on the rare orchid species, the water bodies Glomsjön and Glomsbäcken, and the interaction between golfers and the environment. In addition to written text, the website incorporates photographs taken by us on site as well as audio recordings from the course. This audio-visual approach creates a more dynamic, accessible reading experience. In collaboration with LAGK we also organised a physical exhibition of the images, linking the online and physical elements of the concept.

09
Theoretical perspective
9.1 Hajer's discourse theory

We use Hajer's discourse theory, as described in The Politics of Environmental Discourse, as the theoretical basis to argue that communication of sustainable golf course management practices at LAGK can change golfers' expectations for course aesthetics into eco-friendly practices, and serve as an example for other clubs of how golf can be managed more sustainably — pushing eco-friendly management toward becoming the new norm (Hajer, 1997).

Hajer argues that our perception of an environmental problem — in our case the environmental impact of golfing — is not only determined by science, but socially constructed through discourse. He defines discourse as 'a specific ensemble of ideas, concepts, and categorisations that are produced, reproduced, and transformed in a particular set of practices and through which meaning is given to physical and social realities' (Hajer, 1997, p. 44). A discourse is a specific way of talking and thinking about an environmental issue that shapes people's perception of it. There is currently a dominant discourse among many golfers that the quality of play and aesthetics is more important than the environmental consequences of meeting that demand (Fouillouze et al., 2023). Fouillouze et al. argue this discourse is dominant partly due to a lack of understanding of those consequences.

Discourses can change through the development of new storylines and discourse coalitions. Storylines are simplified narratives that combine ideas, values, and political arguments into a commonly shared story. They are essential for creating discourse coalitions: groups of actors attached to the same storyline who unite in pursuit of discursive hegemony (Hajer, 1997). Applying this, repetition of the importance of eco-friendly course management — on signs, websites, scorecards — can gradually reshape expectations and push for more eco-friendly management at LAGK and other clubs as the new norm. This is what Hajer calls discourse structuration: a new way of understanding an issue becomes socially accepted.

9.2 The SUCCESS framework

For the design of the website elements, we draw on the SciCommercial principles by Finkler & León (2019). This framework extends the six principles of sticky ideas proposed by Heath & Heath (2007) and Shimp & Andrews (2013), known as the SUCCES Framework — Simple, Unexpected, Concrete, Credible, Emotional, Stories — and adds Science as a seventh, producing SUCCESS.

In our project we focused on static images and audio rather than video. This decision was made because another student group worked on a course-history project using video formats. Our collaboration partner preferred a diversity of media on their website. Based on positive empirical findings about images and audio in science communication, we chose this combination, complemented by efficiently used text that creates a narrative.

According to the Dual Coding Theory (Paivio, 1971), multimodal communication is beneficial because cognition operates through two separate but linked systems — verbal/linguistic and visual/non-verbal — and learning is most effective when both are activated simultaneously. Mayer (2009) showed that integrated images and sounds with clear explanations improve comprehension and retention. Sweller (1988) cautions that extra or unclear images can block learning, an effect tied to cognitive load theory: working memory has limited capacity, and overload produces poor understanding and retention.

Jeong & Song (2025) examine the relationship between the eco-friendly management of golf clubs and behavioural intentions of golfers, focusing on the mediating roles of image and perceived quality, and the moderating effect of green marketing. The findings show: (1) green image fully mediates the relationship between eco-friendly management and behavioural intention; (2) perceived quality fully mediates it too; (3) green marketing has a moderating effect. Green image acts as a cognitive filter that lets consumers interpret eco-friendly management as aligned with personal values.

The theory of narrative transportation (Green & Brock, 2000) further highlights that the experience — where attention, emotion, and imagery concentrate on events in a narrative — leads individuals to become immersed, respond emotionally, and form vivid mental images. Unlike traditional persuasion models that require logical evaluation, narrative transportation bypasses analytical defences. Because imagination is occupied, the reader is less likely to counter-argue. This immersive state is effective at shifting beliefs, attitudes, and behaviours.

Principle
Impact on the audience
Context-specific application
Simple
Unconfused
Plain language on signs, single message per panel.
Unexpected
Pays attention
Lead with the orchid count — not the conventional '90 ha protected'.
Concrete
Understands and remembers
Exact figures (1 ha vs 90 ha irrigated) over abstract terms.
Credible
Agrees / believes
Cite Artportalen, IUCN, named researchers — not the club's own marketing.
Emotional
Cares
Photo-led storytelling at human scale: people, flowers, water.
Science
Connects with science
Methods named on the website (Artportalen, geospatial outlier analysis).
Storytelling
Can act on it
Five photo chapters with characters and events, not bullet points.

Table 1 · Adapted by us from Finkler & León (2019, p. 7).

For the sign design, we drew on literature reviews of best-practice scientific visualisation, including infographics and illustrations. According to Perra & Brinkmann (2021), effective visualisations provide clarity for stakeholders and peers, but also act as 'a vessel for story.' In our case the signs depict the topics of the website's stories and link to them directly through QR codes. Fischhoff (2013) argues that collaboration between artists, communication specialists, and scientific experts can accelerate the integration of scientific visualisations and writing — which is why our team brought together natural sciences, science communication, marketing, social sciences, and education.

9.3 Design thinking

Design Thinking (DT) is used as the project approach. DT is user-centred and iterative. Projects begin with an exploratory phase aimed at understanding the problem and context, observing users in real situations, and using these insights to define a problem frame. We met with the club manager and the president of LAGK, and visited the course several times to understand how it is managed. Based on these meetings and observations, we developed our problem frame (Buhl et al., 2019).

The second phase is ideation, where we developed a variety of ideas based on the meetings, modelling, and observations. The third phase is experimentation, where the most promising ideas were selected, prototyped, and tested against predefined criteria. We focused on communication of the sustainability of the course, basing our proposed solutions on academic literature and our own calculations. Solutions were continuously discussed with LAGK during regular meetings throughout experimentation and refined according to their input. We measure success of the project by website traffic and through a questionnaire we plan to send to Marcus and Paul at LAGK.

10
Actors and collaborators

We chose Lunds Akademiska Golfklubb (LAGK) as our primary actor because it is the land user and day-to-day manager of the course — the actor with the most direct influence over what can actually change on site.

We worked with Marcus (CEO of LAGK), Paul (Chairman of the LAGK Directors Board), Victor (Course Manager), and Franz-Michael (Nature Conservation Committee, Deputy in the Directors Board) because they represent different levels of authority and expertise within the club: strategic decision-making, operational management, and ecological responsibility. This combination gave us both practical feasibility and internal support.

Länsstyrelsen Skåne is a second major actor — the legal manager and public authority responsible for the Kungsmarken nature reserve. It issues and enforces regulations, oversees conservation and Natura 2000 obligations, and handles permits and dispensations for activities in the reserve. Since LAGK rents the land from Länsstyrelsen and must apply for permits, this actor defines the legal framework within which the project had to operate.

Lund Municipality is a policy-relevant background actor: the local planning jurisdiction. It is responsible for municipal water planning and stormwater management under the Swedish Environmental Code and the Planning and Building Act. In practice, Lund Municipality oversees surface water runoff, drainage, and groundwater protection around Kungsmarken (Barup & Magnusson, 2017; Lunds Kommun, 2026). We considered these two actors because the project was not only about ecological improvements on the course itself, but how those improvements could be understood and supported beyond the club.

We also included golfers as an important actor group because the long-term success of biodiversity-oriented changes depends on user acceptance. If altered mowing, rewilded areas, or new signs are perceived as reducing playability, they are less likely to be supported. We considered golfers' perspectives as early as possible — the project aimed not only to improve biodiversity but to make sustainability measures acceptable and visible to those using the course.

11
Results

Our project hoped to challenge the perception of golf as inherently careless and environmentally damaging by emphasising sustainability and transparency within golf clubs. We approached this challenge by addressing communication between the golf community and the general public, especially in regard to sustainability.

Through continuous discussion with LAGK we identified several connected opportunities to broaden and improve public discourse around golf and biodiversity:

  • Building a more inclusive community within golf clubs
  • Expanding visitors beyond the golfing community
  • Emphasising sustainability and ecological goals as part of LAGK's identity
  • Increased transparency regarding environmental management
  • Supporting nature exploration and conservation
11.1 Spatial distribution of rare flora

The map in Fig. 1 shows verified observations of rare flora between 1990 and 2026 using data from Artportalen, Sweden's national species observation platform. For our analysis we used only verified observations. Observations were categorised by colour according to IUCN Red List categories and by point size in relation to the number of organisms observed.

Fig. 1
Verified observations of rare flora, Kungsmarken 1990–2026. Point colour follows IUCN Red List categories; point size scales with the number of organisms observed. Two visible clusters: one near Green 12 (left), and one in the eastern reserve (right).
Fig. 2
Kernel density of the same observations. Density is much higher near Green 12 than in the eastern cluster — reframing the 'two hotspots' reading of Fig. 1 as one major and one minor concentration.

Fig. 1 suggests two major outposts of endangered plant observations within Kungsmarken: one located near Green 12 on the western side of the reserve and the other further east. However, density analysis (Fig. 2) shows that these two areas have very different observation densities, with the higher proportion located near Green 12. This indicates that the area surrounding Green 12 should be a priority area for future conservation and management efforts.

A methodological caveat: a portion of the dataset comes from public observation, so there is perception bias — people are more likely to record species in accessible and commonly visited locations (Beck et al., 2014). Future in-field biodiversity assessments should validate these spatial patterns.

11.2 Identification of biodiversity leverage points

In discussions with LAGK, club representatives expressed interest in identifying locations where interventions could most effectively increase biodiversity and improve the public visibility of rare plants. To address this, an optimised geospatial outlier analysis was conducted (Fig. 3).

HIGH-HIGH LOW-LOW LOW-HIGH OUTLIER
Fig. 3
Optimised outlier analysis. Pale red = high-high clusters (statistically expected and confirmed high observation counts). Pale blue = low-low clusters. Intense blue = low-high outliers — areas where rare plants are statistically expected but observations remain low. These are the leverage points for biodiversity expansion.

The pale red hexagons represent areas which are statistically expected to have many rare plant observations and indeed do. Pale blue represents the same for low counts. The important outliers for further decision-making are the intense blue hexagons (low-high outliers): areas where we could statistically expect many observed rare plants, but don't see them in reality. These are the leverage points to expand plant biodiversity in Kungsmarken, and they are targets for our further communication with LAGK.

11.3 Surface runoff and plant distribution

Statistical analysis reveals deviations from expected plant distribution but cannot show causation. Further investigation focused on environmental patterns that may influence biodiversity, with one notable pattern emerging from surface runoff dynamics.

Areas of higher density of rare plants coincide with zones characterised by smaller, more parallel surface water flows instead of concentrated runoff channels (Figs. 4–7). This relationship is most clearly seen in Fig. 5, in which the highest density of rare plants corresponds to diffuse and parallel water flow patterns. Figs. 6 and 7 show concentrated runoff channels associated with low numbers of rare plant observations. Statistically, endangered flora is also more likely to be observed away from concentrated surface streams (Fig. 8). This is one likely factor among several.

Fig. 4
Surface runoff schematic, western reserve. Diffuse parallel flow lines characterising the area around Green 12.
Fig. 5
Plant density overlaid on runoff geometry. The highest density of rare plants coincides with the most diffuse, parallel flow patterns.
Fig. 6
Concentrated runoff zone. A single channel collects water through the area; very few rare plant observations on either bank.
Fig. 7
Concentrated runoff with tributary. The dominant channel and its branch reorganise the local hydrology; rare plant counts remain negligible.
DISTANCE FROM CONCENTRATED STREAM → RARE FLORA OBSERVATIONS →
Fig. 8
Endangered flora vs. distance from concentrated stream. Observations of endangered flora are more probable away from concentrated surface streams. The relationship is correlational, not necessarily causal.
11.4 Comparison to previous habitat assessments

In terms of identifying biodiversity hotspots, our field observation results and the Artportalen dataset align closely. However, these findings differ from the habitat assessment conducted by Länsstyrelsen at the time of the reserve's establishment (Fig. 9). This discrepancy highlights the need for continuous updating of ecological assessments through current observations and research. Reliance on historical classification alone risks losing contextual accuracy and supporting strategic mistakes.

The original habitat assessment by Länsstyrelsen prioritised habitats 6230 (species-rich Nardus grasslands on siliceous substrates) and 6270 (species-rich dry-to-mesic lowland grasslands of Fennoscandian type). In observed reality, those are not the biodiversity hotspots. This underlines one crucial role of research in the decision process: decisions need to be grounded in current data and observations.

LÄNSSTYRELSEN · ORIGINAL 6230 / 6270 OBSERVED HOTSPOTS · 2026 GREEN 12
Fig. 9
Two readings of the same reserve. Left: Länsstyrelsen's original habitat priority (6230, 6270) at reserve establishment. Right: observed biodiversity hotspots from this project's Artportalen and field analysis. The hotspots have moved — or were never where the original framing put them.
12
Communications and outreach

One of the main outcomes of the project was the development of a series of ecologically informational signs, installed across the golf course and nature reserve. The signs communicate findings from the biodiversity and hydrological analyses, including information on endangered plant species, water management, and local ecological processes and pressures.

This communication material was developed in connection with LAGK and designed with both golfers and non-golfing visitors in mind. The signs use maps, photographs (taken by our team), and concise explanatory text to present ecological information in an accessible manner. The material serves to increase public awareness of biodiversity within Kungsmarken and to communicate LAGK's commitment to sustainability and environmental management.

13
Discussion
13.1 The discourse coalition

Selecting a 'positive case' — a club already managing more sustainably than the industry norm — meant the project's interest in reshaping golf's public discourse and LAGK's interest in their own public image converged by default. In Hajer's terms, this is a productive discourse coalition: a coalition of actors who do not share goals but share a useful narrative, holding together long enough to push storylines (Hajer, 1997).

The trap is this: when a science-communication project and a client's PR interest converge without friction, the design has to actively manufacture the friction, or the science-communication function collapses into the marketing function. Jeong & Song's (2025) empirical work on the moderating effect of 'green marketing' is the precise gravitational field this project was working in. The rest of this Discussion examines where the project's choices generated that friction, and where they didn't.

13.2 The pivot as a diagnosis, not a retreat

The project pivoted from a multi-pronged technical scope (SWAT modelling, pathway design, biodiversity, and communication) to a communication-led one with biodiversity analysis as supporting evidence. This pivot is what activates the discourse-coalition reading. The pivot was a diagnosis of where the binding constraint at LAGK actually lay: management practice is already substantially better than the industry norm, so additional technical intervention would have marginal sustainability impact, while the gap between practice and public/golfer understanding is wide.

This is what problem-driven, solution-oriented sustainability science is supposed to do (Clark, 2007; Kates, 2012) — but it commits the project to operating in the discursive arena, which is exactly where the trap sits. The GIS biodiversity analysis is the empirical work that survived the pivot and now does double duty: informing sign placement and grounding the content of the communication outputs.

13.3 Where the design generated friction with the PR framing

Three specific choices in the design resist the collapse into green marketing. First, the decision to communicate the broader sustainability problems of golf — water demand, chemical use, biodiversity loss — and not only LAGK's successes. This is content LAGK's marketing function would not produce on its own. The Pesticide & Fertiliser sign explicitly names what golf courses do in general, before naming what this course does differently.

Second, grounding sign content in the empirical biodiversity analysis — the Artportalen data and the surface-runoff correlation — rather than in generic stewardship language. The cluster near Green 12 is presented as a measurement, not as a claim. Rodríguez Díaz, Bekken, and Metcalfe et al. are cited by name on the website, not as background but as the people whose work the visitor can go look up.

Third, the operationalisation of the SUCCESS framework's 'Science' and 'Credible' principles as constraints on what could be claimed, not just as heuristics for how to claim it. Narrative transportation (Green & Brock, 2000) is a deliberately used but double-edged tool — we used it to make verifiable content more sticky, not to bypass verifiability. The Photo Story chapters carry the emotional load; the Report carries the load that has to be checkable.

13.4 Where the design did not hold the line

Naming these is not self-flagellation but the discipline the through-line of this project demands: a project that critiques alignment-by-default has to be willing to identify where it was complicit in it.

LAGK's gatekeeping of the communication channel — the agreement that LAGK would be the presenter of the information, with no external website — effectively means the project's outputs are mediated by the actor whose image the project also shapes. Then: the absence of direct golfer interviews or surveys before sign design, which meant the audience-facing decisions were informed-based rather than evidence-based, and structurally tilted toward what LAGK believed about its members. The 'ambassador' framing itself has a promotional grammar even when its content is empirically disciplined. And the clubhouse photo exhibition is the project deliverable that sits most clearly inside promotional territory regardless of intent.

In Chambers et al.'s terms, claiming transdisciplinarity at LAGK's design discretion is a partial co-productive agility, not the full version. We did not have an independent audience-side check on the communication design before deployment.

13.5 The Länsstyrelsen finding as methodological mirror

The biodiversity analysis contradicts Länsstyrelsen's original habitat assessment (6230 / 6270 prioritisation). The authoritative state framing has ossified around the assumptions of the reserve's establishment and no longer matches current biodiversity distribution. This is structurally the same move the project is trying to make at the discourse level: refuse to take an authoritative framing — whether from a state actor or from the dominant public narrative about golf — as ground truth, and treat it instead as data subject to revision.

The methodological discipline we applied to Länsstyrelsen's framing is the same discipline we have to apply to our own project's framings, including the 'LAGK-as-ambassador' framing from 13.4. That is what makes the Länsstyrelsen result more than an interesting empirical curiosity — it is the methodological reflection of the project's through-line. (A note on data: Artportalen carries citizen-science perception bias, and Beck et al. (2014) is the relevant caution; the result is robust because field observation aligns with the Artportalen pattern.)

13.6 The measurement gap, honestly

The LAGK questionnaire and website analytics are not yet available. Under the course's process-first grading philosophy, the proper object of evaluation is the design logic itself — but this is not an escape clause. It raises the burden on the design logic, which is what 13.1–13.5 attempted to meet.

Closing the loop would require: a golfer survey after sign installation; comparison of website analytics pre- and post-launch; structured interviews with LAGK after a season of operation; and — the hardest one — some way of testing whether the communication shifted perception among the non-golfer public the project also addressed. The project was transdisciplinary in execution (multiple actor levels, ongoing scope adjustment with LAGK) but the evaluation, in the absence of audience data, is necessarily intra-disciplinary at this stage (Bergmann et al.).

14
References

Selected references cited in the report; the full bibliography is available on request from the project group.

[01]
An, M. et al. (2025). CPM-modelled short-duration precipitation extremes in northern Europe. Climate Dynamics.
[02]
Barup, K. & Magnusson, B. (2017). Stormwater management and the Swedish Environmental Code. Lund Municipality working paper.
[03]
Beck, J. et al. (2014). Spatial bias in the recording of citizen-science observations. Ecological Indicators.
[04]
Bekken, M. et al. Water use on Nordic golf courses. Acta Agriculturae Scandinavica.
[05]
Bergmann, M. et al. Methods for transdisciplinary research: a primer for practice. Routledge / Campus Verlag.
[06]
Bock, E. & Easton, Z. (2020). Nutrient loss from managed turfgrass systems. Journal of Environmental Quality.
[07]
Briassoulis, H. (2011). Opposition to golf-related tourism development: a global review. Tourism Geographies.
[08]
Buhl, A. et al. (2019). Design thinking for sustainability: an analysis of process steps and outcomes.
[09]
Clark, W. C. (2007). Sustainability science: a room of its own. PNAS.
[10]
Eklund, A. et al. (2015). Future precipitation in Skåne under climate change. SMHI report series.
[11]
Finkler, W. & León, B. (2019). The power of storytelling and video in science communication. JCOM, 18(5).https://jcom.sissa.it/article/pubid/JCOM_1805_2019_A02/
[12]
Fischhoff, B. (2013). The sciences of science communication. PNAS.https://www.pnas.org/doi/full/10.1073/pnas.1213273110
[13]
Fouillouze, M. et al. (2023). Golfers' relationships with nature and attitudes about biodiversity conservation. Journal of Outdoor Recreation and Tourism.https://www.sciencedirect.com/science/article/pii/S2213078023000567
[14]
Gebremariam, T. (2024). Insect decline and the role of agrochemicals. Insect Conservation and Diversity.
[15]
Gleeson, T. et al. (2012). Water balance of global aquifers revealed by groundwater footprint. Nature.
[16]
Green, M. & Brock, T. (2000). The role of transportation in the persuasiveness of public narratives. Journal of Personality and Social Psychology.
[17]
Grégoire, G. & Laliberté, J. (2025). Turfgrass management and chemical inputs in temperate climates. Agronomy.
[18]
Hajer, M. (1997). The Politics of Environmental Discourse: Ecological Modernization and the Policy Process. Oxford University Press.
[19]
Heath, C. & Heath, D. (2007). Made to Stick: Why Some Ideas Survive and Others Die. Random House.
[20]
Jeong, J. & Song, J. (2025). Eco-friendly management of golf clubs and behavioural intention. Sustainability.
[21]
Kates, R. W. (2012). What kind of a science is sustainability science? PNAS.
[22]
Keast, A. (2001). Golfers' attitudes to wildlife on courses. USGA Green Section Record.
[23]
LAGK. (n.d.). About the club — nature and history. Lunds Akademiska Golfklubb website.
[24]
Leinauer, B. et al. (2012). Effluent irrigation and salt management on golf course turf. Crop Science.
[25]
Länsstyrelsen Skåne. (n.d.). Naturreservat och Natura 2000-områden i Skåne län.
[26]
Lunds Kommun. (2026). Municipal water and stormwater plan.
[27]
Mayer, R. (2009). Multimedia Learning (2nd ed.). Cambridge University Press.
[28]
Metcalfe, C. et al. (2009). Pesticides, fertilisers, and golf course management.
[29]
Nowak, P. & Rozema, J. (2021). Communicating science through narrative. Diva-portal thesis.https://www.diva-portal.org/smash/get/diva2:1570033/FULLTEXT01.pdf
[30]
Ormiston, J. & Cristol, D. (2025). Comparing biodiversity on golf courses, residential land, and naturalistic sites.
[31]
Paivio, A. (1971). Imagery and Verbal Processes. Holt, Rinehart and Winston.
[32]
Pathak, A. et al. (2022). Pesticide use and ecotoxicity in turf systems. Environmental Pollution.
[33]
Perra, M. & Brinkmann, K. (2021). Visualisations as vessels for story in ecology. Ecosphere.https://esajournals.onlinelibrary.wiley.com/doi/10.1002/ecs2.3786
[34]
Rodríguez Díaz, J. A. et al. (2011). Golf courses and water resources in Mediterranean countries. Agricultural Water Management.
[35]
Romero, C. & Dukes, M. (2016). Are turfgrass irrigation requirements being overestimated? Irrigation Science.
[36]
Ryan, M.-L. (2007). Toward a definition of narrative. In Herman, D. (ed.) The Cambridge Companion to Narrative.
[37]
Salgot, M. et al. (2012). Water reuse for golf course irrigation in Mediterranean countries. Desalination and Water Treatment.
[38]
Sandberg, M. et al. (2016). Allemansrätten and outdoor recreation in Nordic landscapes. Scandinavian Journal of Forest Research.
[39]
Shimp, T. & Andrews, J. C. (2013). Advertising, Promotion, and Other Aspects of Integrated Marketing Communications. South-Western.
[40]
Sweller, J. (1988). Cognitive load during problem solving: effects on learning. Cognitive Science.https://onlinelibrary.wiley.com/doi/10.1207/s15516709cog1202_4

Citations in the text use the author–year style; entries here are abbreviated for readability.

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Use the arrow buttons to switch chapters. Scroll down for the full story.
Kungsmarken meadow at golden hour
Kungsmarken · 90 ha
55.7095° N · 13.2461° E
Chapter 01 — Biodiversity

Where orchids thrive.

Lunds Akademiska Golfklubb is home to more than 400 plant and animal species. As part of the Kungsmarken nature reserve, the course carries the same protection status as the land around it — and its effects are worth both seeing and hearing.

The full story · 01 · Chapter Three

Where orchids thrive

Lunds Akademiska Golfklubb is home to more than 400 plant and animal species. As part of the Kungsmarken nature reserve, the course carries the same protection status as the land surrounding it. Sustainable course management shapes every decision made here — and its effects are worth both seeing and hearing.

Read also

Why don't we pause for a moment on the course? The rough at the edge of the hole is easy to walk past. But when we stop for a few seconds and listen, somewhere in the trees the birds are singing in concert. What thrives here, on and between the fairways, matters as much as what happens on the greens and tees. And what happens here sets LAGK apart from many other golf courses.

Across Skåne, agriculture dominates the landscape.

If we take a look across Skåne's landscape, we see how much of the land is occupied by agriculture. An average Swedish golf course uses approximately 37,500 m³ of water per year, a figure comparable to that of a Swedish farm. Agriculture, however, uses significantly more chemicals per hectare than an average course. In both cases, nature ends up losing. Sustainable course management, as practised at LAGK, shows that it doesn't have to be that way.

Being a member at LAGK is therefore nothing passive: the ecological management of this course is economically and socially dependent on a community who values it. To play here is part of a demonstration that golf and nature conservation can thrive on the same ground — with LAGK showing which steps have to be taken for it.

Franz-Michael Rundquist has been a member at LAGK since 1983. His connection to the course has long extended beyond the game itself. As a Professor of Human Geography, he brought a wealth of historical knowledge. When LAGK's nature committee was formed in 1995, he was involved immediately and has been a central part of it ever since. For decades he has organised cultural and natural-history walks on the course, drawing in both golfers and non-golfers alike.

Asked whether LAGK should be seen primarily as a golf course, a nature reserve, or a historic site, he smiles:

“You're asking the wrong guy. I see all of that. My golf buddies are a bit annoyed with me when I disappear out in the bush and look at some flowers. On the other side, I know the historical aspects of how this whole place has come about and where it stands today.”

In his view, most LAGK members are aware of the conservation work on the course and treat the nature here with care. By providing a home to ten orchid species in total, LAGK also provides a steady food source for pollinators across the entire season.

“Let me draw a picture: if you throw a stone in the middle of a pond, there are waves spreading out. The tours may have an impact in the longer run by influencing more and more people. Swedish golf is quite different from golf in other countries — it's much more democratic in the sense that it covers larger layers of the population.”

Over time, he adds, the walks also reach people who might otherwise never set foot on a golf course, and who come away realising that this is a place they are welcome in.

“A success would be that we are still here and we still have an interesting and important nature to preserve — to continue to preserve. I think we can do that. There are a lot of external factors we can't control, but if we continue the way we do, and with the kind of foresight we can have, I think we are still here and doing quite well.”

LAGK is home to ten orchid species in total, blooming at different points throughout the summer. This staggered flowering means they provide a food source for pollinators across the entire season.

One of the problems that can occur with the flora on the course is people trampling it. A map of Kungsmarken shows that the greatest number of species — orchids above all — occur on the golf course around the hotspot near Green 12.

Species density map of Kungsmarken
Density of endangered species across Kungsmarken — darkest where the hotspot lies.
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Photo · Glomsjön, the source
Glomsjön · the source
55.7081° N · 13.2425° E
Chapter 02 — Water use

Where water stays.

Only the 1.5 ha of greens are irrigated, and every drop is pumped from the on-site lake Glomsjön. The course never touches the municipal supply, so in dry years it competes with no one for drinking water.

The full story · 02 · Chapter One

Where water stays

The full water-use story is being written. It will cover Glomsjön as a closed on-site supply, the choice not to touch the municipal aquifer, and how rain-fed fairways double as habitat.

Full story — coming soon
Read also
Photo · Greens at Hole 7
0 herbicides · site-wide
55.7089° N · 13.2447° E
Chapter 03 — Chemical use

Where less is more.

Fertiliser and pesticide are applied only to the 1.5 ha of greens. No herbicide is used anywhere on the 90-hectare site — the rough, the meadow, and the woodland carry none at all.

The full story · 03 · Chapter Two

Where less is more

The full chemical-use story is being written. It will cover why fertiliser and pesticide are limited to the greens, the complete absence of herbicide site-wide, and what that means for the surrounding habitats.

Full story — coming soon
Read also
01 / 03
Biodiversity Tap to play
§ 04 · Contributors

The people

Six students, four collaborators at the golf club, two agencies, one advisor, and one mentor whose framing the project both relies on and pushes against. Below: who, what they brought, and where to find them.

The student team

Melena Schneider
01 / 06

Melena Schneider

Project & communication lead · Photography · Sign design

Led the project and the communication concept end-to-end. Adapted Finkler & León's SciCommercial principles into the design language used on the signs, narratives, and this website; co-photographed the on-site image collection and designed the three sign concepts installed across the course. Worked on the final report.

Vladyslav Ostroukhov
02 / 06

Vladyslav Ostroukhov

GIS · Hydrology modelling · Photography · Web design

Led the technical half of the project. Designed and ran the geospatial outlier analysis identifying biodiversity hotspots and leverage points near Green 12, and modelled the surface-runoff geometry behind the plant-distribution finding. Co-photographed the on-site image collection. Worked on the final report. Designed and built this website.

Kiki Kristensen
03 / 06

Kiki Kristensen

Sign installation development

Took the three sign designs from artwork to fabrication and into the ground. Specified materials, coordinated with LAGK on permits and placement, scouted the six install locations against the biodiversity hotspot map, and oversaw the physical installation on site. Worked on the final report.

Therese Kjærgaard Ibsen
04 / 06

Therese Kjærgaard Ibsen

Web design · LAGK integration

Collaborated with LAGK to place the information about this project on their website, working with the club to shape how findings reach members and visitors. Designed the web outline for the LAGK website. Worked on the final report.

Jonas Schmitt
05 / 06

Jonas Schmitt

Final report

Worked on the final report — contributing to the writing and analysis behind the team's submitted document.

Oscar Habarta
06 / 06

Oscar Habarta

Field work · Pollinator stories

Helped with field photography work on the course. Prepared parts of the pollinator stories that anchor the narrative side of the project. Worked on the final report.

At the club

MA
CEO
Marcus

Strategic lead at LAGK. Approved the project scope, the sign installations on course, and the clubhouse exhibition.

PA
Chairman, Board of Directors
Paul

Held the long view on the club's nature-reserve obligations. Connected the project to LAGK's earlier conservation history.

VI
Course Manager
Victor

Day-to-day operations. Sign placements were ground-truthed with Victor; the runoff observations align with his field experience.

FM
Nature Conservation Committee
Franz-Michael

Deputy in the Directors Board. Bridged the project to Länsstyrelsen Skåne's regulatory expectations and reserve obligations.

Background actors

LS
State agency
Länsstyrelsen Skåne

Manages the Kungsmarken nature reserve. Sets and enforces the Natura 2000 obligations within which every intervention on this site has to fit.

LK
Municipal authority
Lunds Kommun

Local planning, stormwater, and groundwater protection around Kungsmarken. The framework inside which water moves from lake to greens to runoff to neighbours.

UA
Communication advisor
Ulf Axelsson

Former member at LAGK and teacher in design and photography. Reviewed our communication material and advised on photography storytelling.

BN
Project supervisor
Prof. Barry Ness

Course coordinator, director of the Lund Centre for Sustainability Science. Reviewed and evaluated the project.