Conservation Evidence (2006) 3, 58-60 www.ConservationEvidence.com

The addition of artificial macrophytes to provide macroinvertebrate refugia at Alderfen Broad, , England

Hoare D., Jackson M.J. & Perrow M. Authority, 18 Colegate, , Norfolk NR3 1BQ, UK

SUMMARY

Nylon Italian cobweb brushes were added to Alderfen Broad to provide a refuge for zooplankton and other invertebrates. These were colonised quickly, initially largely by chironomids but then by a greater diversity of taxa. In the second year, there was a vigorous build-up of sponges.

BACKGROUND further inputs of catchment-derived nutrients from entering the broad. Also, in 1992 a The Broads is an area of man-made, suction dredging operation was undertaken to interlinked shallow freshwater lakes in Norfolk remove nutrient rich mud from the bed of and Suffolk, eastern England. There are over Alderfen Broad to reduce phosphorus release 200 km of navigable waterways, with many (which encourages algal growth). more connecting small waterways such as streams and dykes. These link a variety of The purpose of artificial macrophytes: The habitats that support a rich diversity of flora Broads Authority, along with partners (English and fauna, including some of the rarest wildlife Nature and the ), in Britain. The main habitats are the rivers and initiated a project in 2000 to further restore broads (shallow lakes) themselves, fen, carr Alderfen Broad. Nutrient overload (nitrogen woodland and grazing marshes. Much of the and phosphorus) had lead to excessive growth water in the Broads has been affected by of algae and occasional 'blooms' of blue-green excessively high levels of phosphates and algae. The algae, which grew unchecked in the nitrates draining off from agricultural land, and nutrient-rich water, shaded out all other sewage pollution. submergent water plants (macrophytes and charophytes). Without the structure provided The Broads Authority was set up in 1989, with by these plants, invertebrates have nowhere to responsibility for conservation, planning, shelter from predators, and little opportunity to recreation and waterways management. graze on periphyton. Invertebrates such as Restoring water quality is the basis of much of zooplankton provide a critical role in the ongoing conservation work. maintaining water quality by consuming algae, thus preventing other aquatic plants from being shaded out. ACTION Furthermore, with few invertebrates to eat, the Study site: Alderfen Broad (29 ha) is situated fish community was less diverse, which also on shallow fenland peat in a side valley of the had implications for water quality. In a clear- River Ant in . It is a Site of water state there is a variety of piscivorous fish Special Scientific Interest (SSSI). The habitats species (e.g. percids) which in their mature life consist of open water, reed Phragmites stage consume mainly juvenile planktivorous australis swamp and alder Alnus glutinosa carr fish. Having a variety of fish species woodland. Alderfen has been undergoing consuming planktivores releases large habitat restoration following eutrophication zooplankton from predation, which can then caused by decades of excessive imput of control the algae. However, it is important that nutrients derived mostly from water running these juvenile fish, especially perch Perca off heavily fertilised agricultural land. fluviatilis , have sufficient macroinvertebrate prey to enable them to grow fast enough to As part of ongoing restoration work, the inflowing stream was diverted to prevent

58 Conservation Evidence (2006) 3, 58-60 www.ConservationEvidence.com

macrophyte structures increased the potential invertebrate food resource available for perch growth.

Installation of artificial macrophytes: A 30 m2 area was enclosed using temporary plastic ‘fish curtains’ in May 2000. Within the refuge, artificial macrophytes were installed using ‘Italian cobweb brushes’ strung in bunches between posts. (Fig. 1) The brush bristles were made of nylon, roughly 10 cm in length, so each near-spherical brush head had an approximate 20 cm diameter. The handles were about 10 cm long and were used to attach the brushes to each other. Bunches of four plus brushes were suspended by ropes attached to posts installed in the water. The purpose of the brushes was to mimic native plants e.g. rigid hornwort Ceratophyllum demersum which provide zooplankton and other invertebrate Figure 1. Photograph of the Italian cobweb brushes with refugia. used as artificial macrophytes at Alderfen Broad. Sampling of invertebrates: Samples of the aquatic macro-invertebrate fauna were taken complete the developmental dietary change to using a standard protocol developed by become piscivorous. Without piscivorous Jackson (1997). This is a semi-quantitative predators, recruitment of young planktivorous technique using a 1 mm ISO hand-net for a fish is left uncontrolled which leads to high timed period. One-minute samples were taken water turbidity. In other words, the presence of around randomly selected strings of brushes. a healthy and diverse macroinvertebrate After this net sampling, the brushes were community may act as a feedback mechanism pulled out of the water and sessile which helps to stabilise the ecosystem. invertebrates dislodged by vigorous shaking. Similar timed net sampling was also conducted The aim of the Alderfen experiment was to in the surrounding littoral vegetation for determine whether the installation of artificial comparison.

Prosobranchia Pulmonata Hirudinea Asellidae Amphipoda Ephemeroptera Odonata Megaloptera/Neuroptera Trichoptera Diptera

80.0

70.0

60.0

50.0

40.0 % Sample % 30.0

20.0

10.0

0.0 JUN JUL AUG SEP OCT

Figure 2 . The proportions of invertebrate taxa w ithin the Alderfen Broad refugia, June to October 2000 (source : Jackson M.J. 2001).

59 Conservation Evidence (2006) 3, 58-60 www.ConservationEvidence.com

CONSEQUENCES unknown what the impact has been on invertebrate abundance and diversity. In the first five months after installation of the However, a similar project at in artificial macrophytes, the invertebrates inside 2001 (Kelly 2006) also showed that sponges the brush refugia showed a clear colonisation colonised the brushes over time. It is believed pattern, with small grazing chironomids that despite the presence of sponges, dominant early on, with gradual increased invertebrates continue to gain long-term refuge presence of different invertebrate groups, benefit but possibly at a reduced level. Despite notably molluscs and detritus feeders (e.g. some positive outcomes, the use of these water louse Asellus aquaticus ). See Figure 2 artificial refugia is unlikely to be repeated due for proportions of invertebrate taxa within the to short term beneficial nature of the effects, refugia. In the brush refuges, the total number the expense, and the practical difficulties of of individual invertebrate taxa and absolute installation and removal. number of individuals was greater than in the surrounding impoverished natural littoral vegetation. REFERENCES

Invertebrate samples were collected on a Jackson M. J. (1997) Sampling methods for monthly basis the following year but have yet studying macroinvertebrates in the littoral to be analysed. Vigorous build up of vegetation of shallow lakes. The Broads freshwater sponges infested the brushes during Authority, Norwich, UK. the second year, but the impact on total invertebrate numbers and community Jackson M. J. (2001) The importance of compositional change is not yet known. macroinvertebrates in fisheries management of mesotrophic lakes – preliminary report. The Conclusions: The benefit of using cobweb Broads Authority, Norwich, UK. brushes as artificial macrophytes was their initial colonisation by invertebrates. This was Kelly A. (2006) The addition of artificial due to increased surface area available for macrophytes in an attempt to improve water feeding (on algae etc that had colonised) and quality at Barton Broad, Norfolk, England. refugia provided by the brushes. Colonisation Conservation Evidence , 3 , 44-46. by sponges occurred in 2001 and it is currently

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