Showing posts with label Wimbledon Park. Show all posts
Showing posts with label Wimbledon Park. Show all posts

Sunday, 2 August 2020

Blue-green bacteria in the lake

When checking the water clarity on the 30th July I saw a green scum on the surface near the jetties. It looked like blue-green bacteria, so I took a sample for microscopic examination. The scum proved to be mainly a coiled blue-green bacterium (first image). There were smaller amounts of Aphanizomenon flos-aquae (second image) and two or three other species (remaining images below). There are a large number of blue-green bacteria that occur in the UK and it's a specialist matter to identify most species, and beyond my resources. The Environment Agency takes a precautionary approach to blue-green scums, recognising the need to regard all cyanobacterial species and strains as capable of producing toxins, and potentially posing a threat to animal and human health and safety (A DECADE OF MONITORING AND MANAGEMENT OF FRESHWATER ALGAE, IN PARTICULAR CYANOBACTERIA, IN ENGLAND AND WALES. Krokowski, J. & Jamieson, J. 2002). Particular concerns with our lake will be the risk to those undertaking watersports, anglers and, to a lesser extent, the general public on the lakeside path. Some dog walkers encourage their animals into the water, which could put dogs at particular risk.

One can only speculate on the reasons why we have got a bloom this year. Blue-green bacteria thrive in nutrient-rich water in warm summer conditions and it's possible that waterweed clearance has stirred up nutirents normally locked away in the sediments of the lake bed. The lake is already rich in phosphates, but algal growth is probably limited by nitrogen availability. The ability of blue-greens to fix atmospheric nitrogen could be another factor leading to the bloom.


Wednesday, 15 July 2020

July 10th

Today I did the monthly bird count.

The Mute swans are now down to a pair of birds with their eight well-grown cygnets. The lake had a good growth of Fennel-leaved pondweed, despite much having been hauled out by the watersports people. This was being fed upon by the usual Coots. Sixty-five Coots was the third highest July number of the 35-year study, showing that the lake water quality remains good. Most of the 95 Canada geese and 90 Greylag geese were on the lake feeding on waterweed, showing that the grassland of the golf course and great field was not such attractive fodder this year. The Egyptian geese In July, Black-headed gulls that have been unsuccessful in breeding begin to return to the lake and there were 35 birds. Unusually, there was a recently fledged youngster, presumably reared in a nearby area, such as the Wetland Centre. I didn't spot the pair of Common terns, but they were seen regularly in the following days, so still claiming the lake as their territory.

There's now quite a long list of plants growing in the northern part of Horse Close Wood where the Ash trees were cut back in the winter, however the area is dominated by a thick growth of Bramble, Nettle, Hybrid bindweed and Ivy. In most places the other species were struggling for light. Several Ash trees have been coppiced successfully and are putting up vigourous growth, as are a couple of poplars, a few Hawthorns, Wild cherries, Elms and a Horse chestnut. I failed to spot the Hybrid hawthorn under the bindweed and there are no new Oaks to be seen. A Spear thistle and pair of garden escapes (an Argentine vervain and a Large-flowered evening primrose) added colour. Common figwort and Great willowherb were the only wetland species.

The Water-plantain in the brook

Watercress and Great willowherb were flowering in the upstream part of Wimbledon Park Brook, but the real news was in the brook downstream of the cafe. Looking upstream from the bridge, I saw a single plant of Water plantain, an uncommon plant in our area and the first sighting in the public park. It occurs in a few places on the River Wandle. Back before the public right of way across the golf course was closed off, I knew it from the ditches south of the lake. As far as I know it's not found on the golf course any more, but its arrival here suggests that the seeds have come downstream from the lake. Another new species for the public park was near the tennis courts in the far eastern corner: a single clump of the grass Crested dog's-tail. This species is indicative of high quality meadowland, but one plant doesn't prove anything!

National Grid's contractors were working in Revelstoke Road just outside the park entrance. I took a last look at The Glade in Horse Close Wood before National Grid's contractors get going on removing the cables there. I found two new species, bringing the cumulative total seen there since Summer 2016 to 125. These were single plants of the grasses, Tall fescue and Red fescue. Many of the species seen in earlier years have now gone, displaced by taller-growing vegetation. Because of this, the number of species seen in July was just 35 and the number seen at any time in 2020 was 48.

The park seems to have been opened at around 07:30, which is when I spotted the first walker. The two children's play areas had been opened a day or two ago and were now unlocked, although some out-of-date notices suggested not! The worst of the weeds had been cleared before the re-opening. Microbee Tree surgeons were working on the Lombardy poplars at the northern edge of the stadium. This is not best practice, as many bird species are still nesting and it's impossible to spot every nest in such situations.

Sunday, 9 February 2020

The Wimbledon Park Lake Project Flood Study


Commentary on the Wimbledon Park Lake Project Flood Study Stage 2

Summary
The London Study gives options for preventing the Wimbledon Park dam from failing.
Extreme rainfall leads to Wimbledon Park Lake rising so high as to overtop the dam. Overtopping risks failure of the dam, which could quickly release the water of the lake to flood the public park and residential areas between the park and Earlsfield. At worst, the flood would be 3.5 metres (4 yards) deep in the public park and some 1700 buildings would be at risk of flooding. The risk to life requires works to prevent any chance of the dam failing. The study outlines four options to achieve this. Five other options were rejected as impractical.
Option 1 involves reinforcing the lakeside path and the downslope of the dam. To do this, most trees and shrubs on the downslope of the dam would be removed. Much arboretum planting and a singificant part of the ancient Ashen Grove Wood would be lost. This would replace Capability Brown’s 18th century design with a characterless short sward and would harm the habitat of birds, bats and other wildlife.
The other three options all have a large new outfall structure in Ashen Grove Wood to cope with floods from extreme rainfall. Even larger floods would be accommodated by allowing overtopping of a 150 metre (165 yard) long strengthened section of the dam into the area between the watersports centre and the athletics stadium. In these three options, overtopping of the rest of the dam would be prevented by lowering the level of the lake by 35cm (14 inches) and raising the dam by 110cm (43 inches). The height of the dam above the water level of the lake (“freeboard”) would be increased from the present 23cm (9 inches) to 168cm (66 inches). The difference between the three options is in how the dam would be raised. In Option 2, this would be done by adding a 110cm-high wall along the eastern edge of the lakeside path. In Option 3, the lakeside path itself would be raised by 110cm, and in Option 4 a new, low path would be created by infilling a three-metre-wide strip of the edge of the lake, allowing a 110cm-high earth wall (“bund”) to replace the existing path.
All four options are essentially to prevent the dam from failing. They all continue to pass floodwater down into the public park, just in a more controlled way. Reinforcing the path on the top of the dam and lowering of the lake would result in somewhat less (and less frequent) flooding in the public park. In this way, the regular floods that occur would be reduced. However, the downstream effects of extreme rainfall events would hardly be affected.
In Options 2, 3 and 4, replacing the present outfall with the big new one would allow rare floods up to twenty times the capacity of the present outfall to flow into Wimbledon Park Brook. These flows would far exceed the capacity of narrow or blocked pipes in the public park and of the pipe taking Wimbledon Park Brook under the Tube line embankment. There are no proposals in the study for dealing with these downstream problems, nor with the much rarer high floods across the strengthened part of the dam. The brook would need to be opened out and surrounded with a floodplain to cope with these exceptional floods. This would be most readily done if the outfall was moved to near the position of the waterfall. Increasing the capacity of the pipe taking to Brook underground to Earlsfield is the only way to reduce the risk and volume of flooding in the low parts of the public park, but this would transfer the problem to the River Wandle at Earlsfield.
In options 2, 3 and 4 it’s proposed to lower the level of the lake by about 35cm (14 inches). This would take the level down to Capability Brown’s original 1765 design. Brown’s steepened lake edge survives around most of the perimeter of the lake, so lowering the lake by this amount would hardly affect its shape and area. To return fully to Brown’s design, however, would require restoring the lost 120 yards of the southern arm of the lake, and a smaller area lost at the eastern end. The lake has always been shallow, so the effect of the reduced level on angling and watersports would be small. A great benefit of lowering the level of the lake would be to more than double the flood storage capacity of the lake and so reduce the severity and occurrence of regular flooding of the public park by about 90%. The report is deficient in not pointing out that this lowering could be accomplished soon, and cheaply, so providing major benefit and lowering the risk to people and buildings whilst the detail of other measures is being worked up. The report also fails to note that lowering the lake would result in a considerable benefit to the drainage of the golf course and The Wimbledon Club and would virtually eliminate the regular nuisance caused by minor flooding in parts of the public park.
Option 1 and the strengthened section of the dam in the other three Options preserve Brown’s design of the dam. However, Options 2, 3 and 4, raise the dam elsewhere. This would affect Brown’s design and there is little to choose between the three options for this aesthetic harm. Infilling part of the lake for the new path in Option 4 would lose around 1% of the area of the lake.
Merton Council’s Wimbledon Park Masterplan suggests replacing the waterfall with a new “Brownian cascade” outfall. This proposal would preserve the best part of Ashen Grove Wood from a disruptive new construction and would enable the restoration of part of Brown’s lake that was lost when the present outfall was constructed. But this is not considered in the report and the sketch of the replacement outfall in the report would need substantial modification to approximate to a Brownian design. The Masterplan also proposes to move the watersports building and equipment storage to the south corner of the athletics area. This would remove visually intrusive structures that may not be resistant to overtopping floods and enable the replacements to be designed with full consideration of flood safety.
The engineers see such problems with trees on the slopes of the dam that they require them to be removed in Option 1. This is strange, given that built structures on the slopes present similar problems, but there are no proposals in the report to modify or remove them.
The adverse effects of all the proposals on Ashen Grove Wood would remove a woodland screen from one of the few parts of the lake that are distant from light pollution, so affecting bat species that are found there, such as Daubenton’s bat. All options require extensive works on the top of the dam so the existing lakeside trees would be removed. This, also, would harm both amenity and bats.
A detailed design will not be drawn up until an option has been chosen. However, there is no mention in the report of the need to design an outfall structure to enhance the access of elvers to the lake, so as to conserve this threatened species. A crucial detail of Options 2, 3 and 4 appears to have been missed. Raising the existing dam would leave an area on the golf course beyond each end which is not raised. High floods would pass around both ends of the dam and enter the public park in an uncontrolled manner, risking erosion and release of the lake water. I estimate that the erosion protection might need to be extended some 20 metres (22 yards) up towards the golf clubhouse and some 130 metres (140 yards) beside the fence between the golf course and athletics stadium. This would entail an additional cost, especially as it would require land not under the control of LB Merton.
Option 4 is supposed to aid delivery of a project unrelated to flood safety: de-silting the lake. This would deepen the lake and could more than compensate for the lowering of lake level but would be very expensive and intrusive. The report describes this proposal as helping to achieve amenity, ecology and heritage “aspirations” but there is no detail to back up this assertion and it has been challenged. Should costs be saved by using the silt from the middle of the lake to infill the margins of the lake, there would be great harm to the “aspirations”. This would also reduce significantly the storage capacity of the lake, adversely affecting flood safety. The report is seriously deficient in failing to consider this flood storage aspect of Option 4.
Sadly, the stringent engineering requirements cannot be delivered without significant changes to Capability Brown’s dam, so harming landscape amenity, biodiversity and heritage as well as recreational use. I propose an Option 5 that minimises this harm.


Images of the flooding in the public park

Well, my photos didn't seem to attach. Another go now.

Wave overtopping 9th February 2020

9th February 2020

The latest news is that there has been much wave overtopping of the crest of the dam that holds back Wimbledon Park Lake today. This has led to water flowing over the path that runs beside the lake and down into the public park. The main flows through the boat storage and around the watersports building converge on the corner of the bowls green. The green is flooding yet again and some water is also going into the crazy golf area. All this is despite the water level of the lake being quite low. The top of the weir is 23cm below the crest of the dam and the level today is around 22cm down. It would be much worse were the lake more full.