Environment
Loch Tay Environment – General Information
Environment
LTA have taken the progressive step to taking action and study how the healthy the loch actually is. Public information is available from SEPA however the monitoring of the loch and discharges into it is limited and enforcement action can be considered as inadequate.
Our aim is to be a representative body that has first hand knowledge of the loch and data to ensure our representation is acknowledged and acted upon.
Blue-Green Algae
Should you come across issues with blue-green algae. An app was created by the Centre for Ecology and Hydrology which allows users to upload photographs and locations of algal blooms which can then be verified and added to their interactive mapping tool.
Details of this app can be found through the flowing link: Bloomin’ Algae | UK Centre for Ecology & Hydrology https://www.ceh.ac.uk/our-science/projects/bloomin-algae
Bathing Status
Loch Tay is a popular open swimming destination and we are consulting with local swimmers to help protect the loch. More information to follow.
Loch Tay Environmental Issues
Loch Tay Environmental Issues/Impacts and Projects to tackle them.
Background:
Loch Tay has several designated sites:
- Special Area for Conservation (SAC) – covering the whole Tay catchment, designated for: clear water loch (low nutrient status), and lamprey, salmon, otter, freshwater pearl mussel,
- Clear-water lochs with aquatic vegetation and poor to moderate nutrient levels. Both oligotrophic (nutrient-poor) and mesotrophic (moderate nutrient levels) waters, and more rarely may include intergrading types. The dominant substrates of both oligotrophic and mesotrophic waters are silt, sand, gravel, stones and boulders. The clear soft water, which characterizes this habitat type, contains low to moderate levels of plant nutrients and supports characteristic assemblages of plant species. The vegetation community is characterized by amphibious short perennial vegetation the marginal components of which can be exposed on the lake shores during summer.
- Sites of Special Scientific Interest (SSSIs):
- Loch Tay marshes (large open water transition fen – currently suffering from being under grazed leading to encroachment and species loss),
- Morenish meadows (species rich lowland neutral grassland – also under grazed leading to encroachment),
- Carie and Cragganester woods (one of the largest areas of ancient, semi-natural woodland in Perth and Kinross – in poor condition due to bracken dominance),
- Cambusurich Wood (the largest remaining stand of natural, undisturbed woodland along the southern shores of Loch Tay – there is a lack of regeneration of the woodland due to overgrazing by deer and sheep – also some Japanese knotweed on roadside).
- Largest Loch in Pertshire-Depth about 520’ with a fault line running through it from Helensburgh up to Stonehaven
Water: Issues
| Issue | Impact |
| Sewage in burns and loch | health impacts, nuisance, cause of eutrophication; |
| Siltation | blocking ditches and drainage channels, muddying water, cutting light levels, smothering bottom/vegetation (impact on food availability), link to eutrophication (phosphorus is bound to soil particles entering the water)
|
| Eutrophication | in effect adding excessive nutrients to the naturally low levels in the burns and loch leads to freshwater habitat degradation (chemical and physical change), species impacts, algal blooms and excessive weed growth, impacts on water oxygenation levels that impact species such as salmon and trout;
|
| Acidity changes – | impacts on biology and chemistry, release of phosphorus from silt |
| River diversions, abstraction, impoundment and obstructions | (caused by building works, bunds, gabions, jetties, slip ways, dams) – can result in lower/higher and changed timing of water flows, less splash zones in falls, diversion of water courses, loss of water, erosion/siltation, damage to spawning areas, fish migration barriers, amenity impacts of reduced flow (eg: waterfalls), etc |
| Flooding | lack of permanent vegetation cover in the upper catchment leads to a rapid fall and rise of loch level when it rains, change of water flow/river shape, smothering plants, scouring spawning sites, rubbish on shore, road blockages, nuisance to jetties, flood impacts downstream – carse and Aberfeldy; beaver impacts
|
| Fish farm | A rainbow trout farm produces a significant amount of waste, equivalent to the daily waste of around 73 people for every ton of fish produced, according to Global Seafood Alliance. This waste includes both solid waste like uneaten feed and faeces, as well as dissolved waste like nitrogen and phosphorus compounds.
Nitrogen and Phosphorus: For every ton of fish produced, a rainbow trout farm can generate approximately 0.8 kg of nitrogen and 0.1 kg of phosphorus, says ScienceDirect.com. This is comparable to the daily waste output of 73 people producing 250kg Nitrogen and 25 kg Phosphorous equating to 18250 people annually. |
| Sewage | From large Resorts |
Water-Causes of these Issues.
| Cause | Potential Impact |
| Sewage outflow to water bodies | damaged, non-functioning and under capacity septic tanks, use of household chemicals that inhibit proper functioning of septic tanks, not emptied frequently enough, high rainfall flowing into septic tanks via guttering/drains (older systems combine rainwater and household water) leading to overflow directs to water courses during heavy rain. Especially Holiday resorts-KC Taymouth marina. |
| Poor field drainage practices | blocking and unblocking drainage channels, altering natural drainage patterns |
| Farm effluent pollution | silage runoff, slurry storage over flows, yard and machinery washings, poorly designed yard drainage, fertilizer/slurry application timing and methods |
| Fish farm pollution | food pellets/faeces/nutrient/disease/parasites/medicinal chemicals) and escapes – (SEPA 2002 - highly elevated abundances of oligochaete worms, mainly of the family Tubificidae, and showed a considerable shift from the normal fauna of an oligotrophic loch bed |
| Hydro schemes, abstractions for agriculture and water supply | Diversion or water courses etc |
| Upland afforestation | pH, nutrient loading? |
| Beaver impacts on drainage, bank structure
| |
| Siltation from shore-side developments | jetties, landscaping, building works, |
| Erosion of shore and river side – | wash from water craft, access of livestock to burns?
|
Air: Issue
| Issue | Potential/Actual Impact | |
| Particulates/smoke | can have health impacts, nuisance, and lead to deposition of sulphur into water leading to acidification | |
Air: Causes of these Issues
| Cause | Potential Cause |
| Nitrogen air pollution | vehicles, livestock farming, chicken/pig sheds, slurry storage and application, urea fertilizer use |
| Particulates from domestic fires | wood and coal), waste disposal fires, diesel engines, vehicle brakes |
Soil: Issues
| Issue | Potential Cause/ Impact |
| Bank erosion – | wake damage to shore, water level/wind - storm damage, livestock and vehicle poaching/erosion? Can result in increased siltation
|
| Hill erosion | damage to tracks, siltation, landslides, debris on roads/property damage |
| Soil fertility | decline as a result of erosion, increased need for fertilizers, |
| Soil biodiversity | chemical use and ploughing/re-seeding decreasing diversity, |
Soil: Causes of these Issues
| Cause | Impact |
| Soil erosion and run-off | silt and nutrients, re-seeding/ploughing on slopes and/or during high rainfall, soil management, poor design and layout of hill tracks and management (gullies/drains blocked) |
| Bank damage | vehicle and stock access – poor design and management |
Wildlife: Issues
| Issue | Potential cause/Impact |
| Invasives | Japanese knotweed, Himalayan balsam, rainbow trout, Canadian pondweed, Giant hogweed, Rhododendron ponticum, bracken – also possibly Skunk cabbage? Elodea nutallii Nuttall’s waterweed?, North American signal crayfish?– all can lead to habitat degradation, out competing native species, preventing natural regeneration
|
| Diseases | ash dieback, dutch elm, needle blight, Phytophthora austrocedri – juniper, larch. Drummond Hill plantation being cleared for Phytophthora |
| Capercaillie | low numbers due to possible predators, disturbance, deer fencing? |
| Black grouse | decline in suitability of habitat due to loss of woodland edge habitat? |
| Osprey | loss of nesting sites? |
| Raptors | persecution, habitat loss (loss of large breeding trees), trapping, use of poison in the environment? |
| Pheasants and grouse | wild bird impacts, medicinal chemicals |
| Road kill – | Red squirrel, otter? beaver? badger, hedgehog, toad, hare
|
| Bats | habitat degradation and loss, impacts of development on roosting sites |
| Wild Fish Numbers.
| Numbers of salmon and Brown trout decreasing |
Wildlife: Causes of these Issues
| Cause | Impact |
| Land management | Poor domestic and land management phytosanitation and lack of control of invasives once established
|
| Poor sanitation practices | fishers, campers, canoes, SUPs, boats etc |
| Raptor persecution | kites, buzzards |
| Litter |
Habitat: Issues
| Issue | Potential Cause/Impact |
| Physical barriers between land and water | houses, roads, hard standings that disrupt water flow, vegetation spread, animal movement between land and water |
| Tree cover loss | particularly riparian and shoreside – loss of connectivity along lochside, beaver impacts? |
| Meadow and species rich grassland degradation and loss | scrub encroachment due to undergrazing by cattle, over grazing by sheep, seeding and fertilizing leading to species diversity decline, meadow damage by camping/cutting, verge and meadow cutting (no mow May?) |
| Native woodland degradation and loss | felling, fragmentation of woodlands, lack of regeneration, species diversity decline, lack/simplification of ground flora |
| Marshes | degradation and loss of diversity |
| Lead poisoning | from shot and fishing weights |
| State of SSSIs and SAC
| |
| Litter | Cause of death/entanglement |
Habitat-Causes of Issues
| Cause | Impact |
| Livestock overgrazing | over stocking, damaged fencing, tree damage and lack of regeneration, unmanaged access to water bodies, poaching riparian areas |
| Deer overgrazing | over stocking, inadequate fencing |
| Tree loss and woodland degradation | camping/firewood cutting, built developments, bracken invasion |
| Scrub encroachment into meadows/grassland | lack of cattle grazing, winter disturbance |
People: Issues
| Issue | Potential cause/Impact |
| Noise | motors/music, hydro schemes – nuisance |
| Light pollution | clear sky, disrupting wildlife breeding, nuisance, |
| Smell | sewage, fish farm, vehicle fumes, dead stock, coal fires |
| Human and dog waste | plastics/glass/rubbish, nuisance, health, pollution, smoke from burning of rubbish, dog bags left on paths and thrown into neighbouring fields and gardens |
| Wild fires | damage, risk of spread |
| Road accidents | cars, deer, livestock, cyclists and walkers |
| Amenity/visual – | excessive road signage (eg: at Kenmore beach turning)
|
| Cultural heritage | archaeological site damage from eg: forestry, poor access and signage to some sites? |
| Restricted access to shoreside and burns | |
| Point sources of pollution | fly tipping and rubbish dumping |
| Herbicides and pesticides pollution | damage to native flora and fauna, pollution to water bodies |
| Salt from roads | run-off to water bodies, damage to plants? Road runoff tends to contain a number of pollutants including sediments, hydrocarbons (from oil and fuel) and metals such as iron, copper and zinc from wear of car parts. Particulates can include carbon, rubber, plastics, grit, silt, rust and metal filings. In winter, especially in Scotland, road runoff often contains de-icing salt. Impurities in rock salt can include metals such as cadmium. Road salt may enhance release of toxic metals from sediments. Transport for Scotland |
People-Causes of these Issues
| Cause | Reason/Impact |
| Improper herbicide and pesticide use | application during wind/rain, over use, use near water courses |
| Power vessels | noise, wakes, fuel spills |
| Motor bikes | noise, exhaust pollution, seem to be using south side of loch more now |
| Vehicle access to water bodies | erosion, pollution, habitat damage |
| Building development | building works and post-build impacts, erosion, pollution, waste management, tree and habitat loss, flooding/hard standings/drainage, septic tanks, wildlife movement barriers |
| Camping | waste, tree cutting, fire, vehicle damage to soil/flora |
| Gravel extraction
| |
| Greylag geese | can cause local nutrient loading and meadow damage |
| Access restrictions | due to fencing
|
| Dog walkers | dog shit bags left in trees, fields and gardens |
| Visitors | litter |
| Traffic | 1. accidents, using passing places to park, parking to camp
|
Climate: Issues
| Issue | Potential cause/Impact |
| Emissions | from residents, traffic, housing |
| Opportunities to develop renewables | |
| Adaptation | what can we do to prepare for climate change impacts – higher rainfall, storms, flooding? How can we also help alleviate climate impacts on habitats and wildlife?
|
Climate: causes of these Issues
| Cause | Reason/Impact |
| Higher emissions than average | in rural areas due to reliance on oil and LPG, lack of public transport, old housing stock |
People: issues
| Issue | Reason/Impact |
| Improper herbicide and pesticide use | application during wind/rain, over use, use near water courses |
| Power vessels | noise, wakes, fuel spills |
| Motor bikes | noise, exhaust pollution, seem to be using south side of loch more now |
| Vehicle access to water bodies | erosion, pollution, habitat damage |
| Building development | building works and post-build impacts, erosion, pollution, waste management, tree and habitat loss, flooding/hard standings/drainage, septic tanks, wildlife movement barriers |
| Camping | waste, tree cutting, fire, vehicle damage to soil/flora |
| Gravel extraction
| |
| Greylag geese | can cause local nutrient loading and meadow damage |
| Access restrictions | due to fencing
|
| Dog walkers | dog shit bags left in trees, fields and gardens |
| Visitors | litter |
| Traffic | 2. accidents, using passing places to park, parking to camp
|
Projects that LTA are developing to tackle some of these impacts and their causes:
| Project | Action |
| SEPA water quality monitoring | FreshWater watch (N/P testing starting April 2026) |
| Bathing water status | Via Surfers for sewage and cold water swimmers |
| Check Clean Dry campaign | awareness and advice on preventing introduction on non-native invasives |
| Invasives eradication campaign | mapping, advice to land managers, eradication projects, |
| Septic tank campaign | mapping and registering, inspection, joint emptying, grants for improvement, advice on living with a septic tank, supply of septic tank appropriate household products |
| Litter | beach clean-up days, roadside bins, returnable/deposit bin bags with fishing licenses, recycling points (Kenmore, Killin, Lawers?); bins at camp spots; portaloos |
| Roads:
| Safety: 30 mph limit on south side road, extend 20 mph from Kenmore to Dalerb and Acharn and Killin to Firbush; 20 mph along Rob Roy Way on road sections (Ardeonig to Acharn); road signage; passing place improvements; wildlife passes/signs;
|
| EV charging points | Kenmore, Acharn, Lawers, Dalerb, Ardeonig, Ardtalnaig |
| Parking | on-field parking in summer? Signage to prevent kerb-parking; police patrols? |
| Replace rock salt | at sensitive sites?
|
| Reduce verge cutting frequency | other than for safety concerns |
| Tidy up road signs at Kenmore beach | |
| Energy efficiency:
| Warm Connections advice
|
| Farming:
| Checks on Water quality |
| Land management | Hill track design and management. Promote best practice, ensure Local Authorities enforce Prior Notification SELINK campaign |
Loch Rannoch & Loch Tummel Partnership
Loch Rannoch & Loch Tummel Partnership
The LRCA is a company, but not a charity. The Loch Tay Association is an informal Association. i.e. neither a company nor a charity.
- b) The concerns for each Loch
Loch Tay - there are concerns over chemical pollution due to the fish farm and sewage outflows. There have been regular algal blooms. Anecdotal evidence point to a reduction in fish numbers and insect numbers. The Loch Tay study will create a baseline of phosphate and nitrate pollution for a long term study. (John Cassidy will be able to provide technological help with sensors). Loch Tay is not a Hydro Loch and so changes in loch level are natural and are not of a major concern. Samples of water will be taken from 12 sites around the loch and Citizen Scientists will be trained by ‘Freshwater Watch’ https://www.freshwaterwatch.org/pages/about-us
Loch Rannoch - there is concern about the rapid changes in loch level caused by electricity demand as it is a Hydro Loch. John Cassidy will be able to provide technology to track water levels. Citizen Scientists will assess insect larvae at sites (number to be decided) around the loch. They will be able to use a machine learning program, created by John Cassidy, to allow them to identify caddisflies from photographs taken on their phones.
The sites used will be, in part, determined by the vegetation on the shores. John Cassidy can use his drone to identify tree types.
The LRCA is also concerned with water quality but Loch Rannoch has not experienced the algal blooms that occur on Loch Tay.
- c) Use of Technology to gather data concerning the health of each loch
Sensors - Nitrate, Phosphate, Water Level, LiDAR
- d) The involvement of Citizen Scientists in each study
The Loch Tay project is going to use the ‘Freshwater Watch’ training and protocols.
The Loch Rannoch project is going to use the ‘’Riverfly’ training and protocols and is considering also using the ‘Freshwater Watch’ training and protocols.
Contact has been made with Kelly Dodds for the instigation of ‘Riverfly’ training.
The Riverfly Partnership - https://www.riverflies.org/
- e) Public enagagement -
Local publications, word of mouth and social media will be used to recruit Citizen Scientists from the following demographics -
Riparian Owners, Visitors, Residents, Fishermen, Schools (both primary and secondary).
The intention is to engage people irrespective of whether or not they volunteer to be citizen scientists.
From the LRCA point of view this will begin with a campaign to recruit people to be ‘Friends of Rannoch’. Some of these supporters may then volunteer as Citizen Scientists for the project.
- f) The possible expansion of the twoprojects to become three, with the inclusion of Loch Tummel.
It was felt that pressure to ensure water quality that came from those concerned about three different, but adjacent Lochs, would carry weight with, SSE, SEPA and the Government. Colin Stanfield will be contacted, as he is on the Killiecrankie, Fincastle and Tummel Community Council, to assess whether residents there would be in favour of joining in with the Loch Rannoch and Loch Tay associations in their projects.
Next Friday John Cassidy is meeting with John Swinney (First Minister) to discuss the factors governing water quality across the Highlands. He will mention the Projects.
Richard Paul will supply the Loch Tay Association with a list of potentially useful contacts.
The Loch Rannoch and Loch Tay Associations agreed that continued cooperation would be mutually beneficial as they share common aims of achieving unpolluted freshwater and high biodiversity. They also like a degree of cooperation with HPCLT where their aims were convergent as in water quality and maintaining biodiversity.
Below - a comparison of the Riverfly Partnership and the Freshwater Watch methods and protocols for citizen scientists.
A comparison of the methods used by Freshwater Watch (FWW) citizen scientists, how they are trained, and how this contrasts with the Riverfly citizen science methods and training used in the UK.
Freshwater Watch (FWW) — Methods & Training
Methods Used
Freshwater Watch is a global citizen science water quality monitoring programme run by Earthwatch Europe that focuses primarily on water chemistry and contextual observations. Citizen scientists use standardised protocols to collect data that supports scientific research and local decision-making.
Key components of FWW methods include:
- Water chemistry testing:
- Nitrate and phosphate measurements using low-cost colourimetric kits (e.g., Griess reaction for nitrate; enzymatic phosphate tests). Volunteers compare colour changes to charts to estimate nutrient levels.
- Turbidity measurement using a Secchi tube to estimate suspended matter.
- Ecological and contextual observations:
- Bank vegetation, waterbody type, presence of wildlife, visible pollution evidence, recent rainfall, and land use within a set radius.
- Hydrological estimates:
- Flow category (e.g. slow vs steady), water level classification and photographic records.
- Use of technology:
- Data are often recorded via the FWW app, which geo-tags and timestamps samples, and uploads results to a global database with real-time feedback.
Purpose: FWW provides broad water quality indicators (nutrients, turbidity, and observational context) that can inform local environmental action and contribute to larger datasets for scientific and policy use.
Training for FWW Volunteers
- Train-the-Trainer Model:
Project leaders (community group leaders) are trained by Earthwatch scientists. They, in turn, train local volunteers in person. - Training Materials:
Participants receive manuals, videos, quizzes, and printed instructions with their kit. Training covers sampling procedures, safe handling, how to use test kits, and how to enter data. - Support & Quality Control:
- Data submissions are automatically checked for internal consistency by the online system.
- Participants get immediate feedback via the app after uploading.
- Project leaders and Earthwatch staff review datasets and follow up on anomalies.
- Accessibility:
FWW emphasises that no prior scientific experience is required and training is designed to be inclusive and user-friendly.
Riverfly Citizen Science — Methods & Training
Methods Used
The Riverfly Monitoring Initiative (RMI) is part of the Riverfly Partnership and centres on biological monitoring rather than direct chemical testing.
Core elements of Riverfly methods include:
- Macro-invertebrate monitoring:
Volunteers sample riverbed invertebrates that are indicators of water quality (especially sensitive groups like mayflies, stoneflies and caddisflies). - Kick sampling:
Volunteers use a standard net to disturb the riverbed for a timed period (typically 3 minutes) to collect invertebrates, followed by a 1-minute stone turnover to sample those clinging to substrates. - Identification & scoring:
Monitors identify and count eight key invertebrate groups and derive an RMI score. This score is compared to a “trigger level” set for each site to detect sudden declines potentially indicating pollution. - Variants:
There are Urban Riverfly and Extended Riverfly options which include additional taxa, with Extended giving a more detailed picture of river stressors.
Purpose: Riverfly methods provide an early warning biological indicator of water quality, often triggering official investigation if thresholds are breached.
Training for Riverfly Volunteers
- Our Contact is Kerry Dodd (Email Kerry.Dodd@buglife.org.uk )
- Accredited Training Courses:
Volunteers receive formal, accredited training through Riverfly Partnership hubs coordinated locally. - Training Format:
A typical training session includes a theory component (usually morning) on invertebrate ecology and identification, followed by a practical session (afternoon) at the river where sampling and identification are practised. - Certification:
After completing the training, volunteers are considered certified Riverfly Monitors and can collect and submit data. - Ongoing Support:
Local coordinators and the Riverfly Partnership provide ongoing support, refresher training and advanced courses (e.g., Extended Riverfly) for more detailed work. - Skill Requirement:
Identifying invertebrates to the correct group requires careful observation and often some practice; training ensures volunteers are competent before they survey independently.
Comparative Summary
| Aspect | Freshwater Watch (FWW) | Riverfly Monitoring |
| Focus of Monitoring | Water chemistry (nutrients, turbidity) + contextual ecological observations | Biological community health via macro-invertebrates |
| Data Collected | Quantitative nutrient/turbidity estimates + visual/risk context | Invertebrate counts and presence/absence leading to RMI scores |
| Equipment | Chemical reagent kits, Secchi tubes, smartphone/app for data upload | Kick net, trays, magnifiers and ID guides |
| Training Model | Train-the-Trainer; in-person local training with manuals/videos | Accredited in-person workshop with practical field component |
| Required Skills | Basic procedures and safety; minimal prior experience needed | Detailed biological identification skills; more technical |
| Quality Control | Automated app checks + leader and Earthwatch review | Certification and structured support via coordinators |
| Primary Use of Data | Broad water quality assessment and trends | Early warning of pollution and long-term biological health |
Key Differences in Approach
- Conceptual focus: FWW is chemistry and context heavy; Riverfly is biology and biodiversity oriented.
- Training depth: Riverfly training tends to be more formal and technical, focusing on species identification, whereas FWW training prioritises accessibility and standardised procedures for chemical monitoring.
- Data interpretation: FWW provides direct field results fed back to volunteers instantly; Riverfly outputs are biological scores requiring context (trigger levels) set by ecological contacts.
Press Releases & News
Press Release - 8th January 2026
Loch Tay Community Launches Ambitious Water Testing Project to Safeguard the Future of the Loch
Loch Tay, Scotland — A powerful new community-driven initiative is set to transform how Loch Tay’s water health is understood and protected. The Loch Tay Association has announced the launch of its Water Testing Project, an ambitious citizen-science programme designed to shine a light on growing environmental pressures affecting one of Scotland’s most cherished lochs.
Although Loch Tay’s waters may look pristine, early signs tell a different story. Increasing levels of sediment and nutrients—particularly nitrates and phosphates—are beginning to threaten aquatic life, water clarity, and the delicate balance of the wider ecosystem. Yet with limited official monitoring in place, the true scale of the issue remains unclear.
That is about to change.
Community Volunteers Take the Lead
At the heart of this project is the creation of the Loch Tay Water Quality Monitoring Group, a dedicated team of trained local volunteers who will carry out regular, scientifically robust water testing across the loch. Using validated tools and easy-to-use methods, volunteers will track key indicators of pollution, including Nitrates, Phosphates and Turbidity These vital measurements will help identify pollution sources, reveal patterns over time, and build a comprehensive evidence base to guide future action.
Learning from Success: The Windermere Model
The project draws inspiration from the breakthrough citizen-science efforts at Lake Windermere. There, local people partnered with Freshwater Watch, uncovering serious pollution issues that had gone undetected by limited official monitoring. Their work ultimately prompted renewed attention and meaningful intervention.
Now, Loch Tay is poised to follow that successful path. By joining forces with Freshwater Watch, the Loch Tay community will gain access to expert training, high-quality testing kits, and global data platforms—empowering local residents to become guardians of their own waters.
This project marks a significant and proactive step forward. By combining community passion with scientific rigour, the Loch Tay Association aims to generate the most comprehensive picture ever assembled of the loch’s water quality—and ensure that any emerging issues can be tackled early and effectively.
“This is about taking ownership of our loch’s future,” said Bill Oppenheimer Chair of the Loch Tay Association. “By coming together as a community and working with respected scientific partners, we can protect this extraordinary place for generations to come.”
For more information on becoming a member of the Loch Tay Association or to volunteer with the Water Quality Monitoring Group, please contact:
Loch Tay Association Secretary Email: wilmakenmore@hotmail.com
AGM 2026
If you love Loch Tay. We need your help.
You can help us by becoming a member and by coming along to our AGM on Monday 16th march at 1800hrs in the Reading Rooms Kenmore
Loch Tay is the heart of our community, but beneath its pristine surface, the water is fast arriving at a tipping point.
From devastating diesel spills and sewage incidents to the surge of invasive species and choking algal blooms, the warning signs are clear. Nutrient levels are climbing, threatening the clarity and life of the loch we love. With limited official monitoring, the responsibility to protect this magnificent asset falls directly on us.
The Loch Tay Association is stepping up, but our impact is limited by our numbers. To fight back, we need more than just passion—we need a stronger mandate and the funds to take action. Your membership can help change this.
This year, our volunteers are launching a year-long water testing project to establish a vital data baseline. that may provide the undeniable evidence needed to force meaningful intervention from environmental agencies.
Don’t let Loch Tay’s beauty become a memory. Join us today. Your small annual contribution is the investment our loch deserves.