B. A. Whitton

The Trophic Diatom Index: a new index for monitoring eutrophication in rivers

A index for monitoring the trophic status of rivers based on diatom composition (‚trophic diatom index’, TDI) has been developed, in response to the National Rivers Authority (England & Wales)s needs under the terms of the Urban Wastewater Treatment Directive of the European Community. The index is based on a suite of 86 taxa selected both for their indicator value and ease of identification. When tested on a dataset from 70 sites free of significant organic pollution, this index was more highly correlated with aqueous P concentrations than previous diatom indices. However, where there was heavy organic pollution, it was difficult to separate the effects of eutrophication from other effects. For this reason, the value of TDI is supplemented by an indication of the proportion of the sample that is composed of taxa tolerant to organic pollution.The index was tested on the R. Browney, N-E. England, above and below a major sewage discharge. TDI values indicated that the effect of inorganic nutrients on the river downstream of the discharge was slight as the river was already nutrient-rich, but there was a large increase in the proportion of organic pollution-tolerant taxa. This indicates that the river was already so eutrophic upstream of the discharge that tertiary treatment to remove P would not be effective unless other aspects of the discharge were also improved.

NITROGEN AND PHOSPHORUS IN EAST COAST BRITISH RIVERS: SPECIATION, SOURCES, AND BIOLOGICAL SIGNIFICANCE

The data on nitrogen and phosphorus fractions obtained during the core study programme of the Land Ocean Interaction Study for rivers draining the central part of eastern UK are presented and assessed with respect to sources and potential biological effects. The approaches used include comparisons of: (1) overall speciation of nitrogen and phosphorus in the rivers by examining average values and ranges; (2) relationships between nitrogen and phosphorus fractions and flow; and (3) relationships between nitrate and total dissolved nitrogen and soluble reactive phosphorus and total dissolved phosphorus. In addition, comparisons are made between data from the LOIS study region and literature on rivers elsewhere in Europe and North America. Detailed consideration is given to N/P mass ratios in river water, because these can indicate conditions of potential N- or P-limitation for algal and other plant growth. A mid-river site in the Ure, a tributary of Yorkshire Ouse, showed 44% of samples with a N/P mass ratio of>24. Comparison of records for the `growing season (April to September), when algal and other plant activity is highest, with those from the `dormant season (October to March) showed a much higher N/P mass ratio during the growing season, indicating that conspicuous growths of Cladophora glomerata and other submerged plants may be reducing ambient phosphate to levels of marked phosphorus limitation.

Comparative performance of benthic diatom indices used to assess river water quality

The performance of five types of benthic diatom index (four quantitative methods and a zoning system) to evaluate water quality was tested in rivers in England and Scotland. Significant correlations were observed between the four quantitative indices examined. In the case of SPI (Specific Pollution sensitivity Index) and GDI (Generic Diatom Index), over 80% of the variation in GDI was explained by a bivariate regression on SPI. Samples taken from six sites at four different times of year showed no significant influence of season on any of the indices. The zoning system led to a similar assessment of organic pollution as the SPI and GDI indices , but it was sometimes difficult to determine the zone. This method showed no obvious advantages over the quantitative indices. The high correlation between values for indices based on species and those on genera suggests that for routine monitoring, recognition to the generic level is adequate.

Biology of the freshwater diatom Didymosphenia: a review

Features of the colonial diatom Didymosphenia are reviewed, especially D. geminata. Although there is a long record of its occurrence in north temperate regions, mass growths have been reported much more widely in recent years. Contrary to some statements in the literature, there are also reliable older records for the southern hemisphere, though the first report of mass growth was in New Zealand in 2004. The annual cycle of morphological changes in D. geminata in northern England, and probably elsewhere, includes a winter period when motile cells are attached to the substratum followed by spring when stalks start to develop. These raise cells into the water column and provide a site for phosphatase activity. Environmental factors associated with success include absence of extreme floods, high light, pH above neutral and nutrient chemistry. D. geminata often, but not always, occurs in waters where the N:P ratio is high for much of the year, but the key factor is the ratio of organic to inorganic phosphate. D. geminata thrives where organic P is predominant and the overall P concentration is low enough for organic P to be an important P source. It is unknown whether organic N can be used. Environmental changes increasing the relative importance of organic P are likely to favour D. geminata. Likely examples are increased N:P due to atmospheric N deposition and changes in form and seasonality of P release from organic-rich soils due to climatic warming. The nutrient chemistry of deep water released from dams to rivers also needs investigation. To what extent are genetic changes occurring in response to environmental changes and are new ecotypes spreading round the world? In spite of many adverse reports about D. geminata, such as detached mats blocking water pipes, there is still doubt about the extent to which it causes problems, particularly for fish. There have been few adverse effects on migratory salmonids in Europe and North America, but at least one report of harm to a brown trout population in USA. In New Zealand, it has caused serious problems for water sports, although it remains open to question how much adverse effect it has had on fish populations. If the presence of microcystins in or associated with D. geminata, as indicated recently for two populations, proves to be widespread and at sufficiently high concentration, their possible accumulation in fish requires study. Where control is required, this could be achieved by enhancing the ratio of inorganic to organic phosphate in the water early in the growth season. Practical ways to achieve this are suggested.

Accumulation of heavy metals by aquatic mosses. 2: Rhynchostegium riparioides

A study was made of general ecology and metal accumulation in the widespread aquatic moss Rhynchostegium riparioides, (Hedw.) C. Jens. with a view to developing the use of this species as a monitor of heavy metal pollution. In order to establish a data bank for statistical analysis, samples of water and moss were taken within a 6-week period from 105 sites (10-m reaches) in Northern England from streams and rivers of diverse physical and chemical types. Analyses were made of 14 metals (Na, Mg, K, Ca, Cr, Mn, Fe, Co, Ni, Cu, Zn, Cd, Ba, Pb) in both 2-cm tips and whole plants. The same 14 metals were also measured in both total and filtrable water, together with 12 other variables. Samples of tips were easier to prepare for analysis, but had significantly (p < 0.001) lower concentrations of all metals except Na and K. Significant correlations (p < 0.001) between metal in moss and aqueous metal were found for ten metals (Na, K, Mg, Ca, Mn, Cu, Zn, Cd, Ba, Pb). Correlations between metals in moss and in water were in general similar for tips and whole plants, but much higher for tips with Na, Zn and Cd; the relationship was quite similar whether total or filtrable water was considered, with the exception of Ba where the correlation was much higher with the latter. A multiple regression was used to suggest which variables in water and/ or moss may influence accumulation of Co, Ni, Cu, Zn, Cd, Ba and Pb in the moss. For instance, the variables which had a very highly significant effect on Pb in tips were Pb, filtrable reactive phosphate and Zn in the water. A discussion is included of how the data may be used for monitoring purposes.

Accumulation of heavy metals by aquatic mosses. 1: Fontinalis antipyretica Hedw.

An account is given of methods developed to monitor heavy metals in rivers by measuring the concentration of these metals in Fontinalis antipyretica Hedw. Key features of the standard method recommended include the harvesting of materials from microhabitats with fast current speeds wherever possible, thorough washing in field and laboratory, use of terminal 2-cm lengths of shoot, drying at 105°C and digestion in 2 M HNO3. In order to establish the extent to which this species is useful and to provide baseline data with which others can compare their own observations, samples of moss, water and sediments were harvested for analysis from 52 different sites in northern England and Belgium. Significant positive correlations were obtained between Cu and Zn in 2-cm tips and in both (total) water and sediment, but in the case of Cd and Pb only between 2-cm tips and sediment. Multiple stepwise regression was used to quantify the apparent influence of environmental variables. For instance, with Pb in the moss as the dependent variable, significant influences were found for Zn in the moss (+ve) aqueous Mn (+ve) and filtrable reactive phosphate (−ve). Variables which were significant were incorporated in each case into equations to predict the concentration of metal that would be expected if allowance was made for the concentrations of all these variables at each site. In the case of Pb, r2 = 0.075 for metal in moss versus aqueous metal, whereas r2 = 0.879 for metal in moss versus the predicted value for metal in moss. This suggests that the lack of correlation between Pb in moss and Pb in water was probably due largely to the influence of other variables. For Cd, the difference was less: r2 = 0.013 and r2 = 0.47, respectively. A principal components analysis was also carried out, with measurements of water and moss as the variables ordinated. An example is given of the use of the moss to monitor intermittent Zn pollution in R. Wear.

Heavy metals in water, sediments and invertebrates from a metal-contaminated river free of organic pollution

A study was made of water, sediments and invertebrates in the R. Derwent, North-East England, at one site above and three sites below a stream bringing in high concentrations of Zn, Cd and Pb derived from an active fluorspar mine. The mean concentrations of these metals in filtrable water at the unpolluted site were 0.020, <0.0003, 0.005 mg l-1, respectively, while those at the first polluted site were 0.29, 0.0006, 0.016 mg l-1. The benthic macroinvertebrate fauna was dominated by insects; all taxa present at the unpolluted site were represented at one or more of the polluted sites. In almost all cases the elevated concentrations of metals in water and sediments at polluted sites were paralleled by higher concentrations in animals. Significant positive correlations were demonstrated between metal concentrations in certain taxa and those in their environment e.g. Ecdyonurus venosus and aqueous Pb. Mayflies tended to concentrate Zn, Cd and Pb to higher levels than other groups. Comparison of carnivorous species with other taxa revealed no indication of increased metal concentrations at higher trophic levels.

Importance of organic phosphate hydrolyzed in stalks of the lotic diatom Didymosphenia geminata and the possible impact of atmospheric and climatic changes

The aquatic colonial stalked diatom, Didymosphenia geminata, has acquired notoriety in recent years because of huge increases in many rivers of temperate regions. However, in some streams in northern England it has probably or, in the case of the R. Coquet (Northumberland), certainly been abundant for many decades. The paper describes the nutrient environment and phosphatase activities of Didymosphenia in Stony Gill (N. Yorkshire), a fast-flowing stream draining an upland catchment with peaty soils overlying limestone. Organic phosphate formed 85% of the filtrable phosphate in the water during the study (January–August 2000), with a maximum in April. Colonies were most abundant in June, but had disappeared by August. Surface phosphomonoesterase (PMEase) and phosphodiesterase activities assayed from March to July showed low PMEase activity in early March, but otherwise both were high throughout the period and especially so in June and July. Use of BCIP-NBT staining procedure showed that PMEase activity occurred in the stalks. A more detailed study of colony structure and staining with material from the R. Coquet in June 2006 also showed marked PMEase activity, with staining localized in the upper part of the stalks and the cells remaining unstained. It is suggested that organic phosphate is hydrolyzed in the stalk and the inorganic phosphate passes to the cell via a central tube in the stalk. It seems likely that organic phosphate as a major P source is a key factor favouring the success of Didymosphenia. The possible impact of environmental changes in the catchment such as climatic warming, C loss from peat and atmospheric N deposition is discussed.

Interspecific differences in Zn, Cd and Pb accumulation by freshwater algae and bryophytes

The relationships between the concentrations of zinc, cadmium and lead in aquatic plants and the concentrations of these metals in the ambient water have been compared for three algae (Lemanea fluviatilis, Cladophora glomerata, Stigeoclonium tenue), one liverwort (Scapania undulata) and three mosses (Amblystegium riparium, Fontinalis antipyretica, Rhynchostegium riparioides). The data to establish these relationships are all based on our own studies, some published already, some here for the first time. They come from a wide range of streams and rivers in Belgium, France, Germany, Ireland, Italy and the U.K. There were significant bivariate positive relationships between concentrations of Zn, Cd and Pb in water and plant for all species except Cd and Pb in Stigeoclonium tenue. When relationships were compared using datasets with total or filtrable metals in water, most differences were slight. However there were marked differences both between species and between metals. Comparison for the seven species of Zn in the plant when aqueous Zn is 0.01 mg l−1, a concentration at which all seven were found, shows that the four bryophytes had the highest concentrations; however the two green algae had steeper slopes (representing change in concentration in plant in response to change in aqueous concentration). Lemanea fluviatilis had a slope closer to that of the bryophytes, but the concentration was about one order of magnitude lower. All seven species were found at a concentration of 0.01 mg l−1 Pb, and at this concentration there were almost two orders of magnitude difference between the species which accumulated the most (Scapania undulata) and the one which accumulated the least (Cladophora glomerata). The steepest slope was however shown by C. glomerata.When multiple stepwise regression was applied, the aqueous metal under consideration was the first variable extracted in only nine of the 21 regressions. However one of the other heavy metals (aqueous or accumulated) was extracted first in all but one of the other regressions, presumably because the occurrences of Zn, Cd and Pb were strongly cross-correlated. The principal non-heavy metal factor extracted for Zn and Cd, but not Pb, was aqueous Ca. The relevance of these results to the use of aquatic plants for monitoring heavy metals is discussed.

Enteromorpha as a monitor of heavy metals in estuaries

An account is given of the use of Enteromorpha to monitor zinc, cadmium, mercury and lead pollution in six estuaries and the British North Sea coast. The ranges for each element were: Zn, 19–437 µg g−1; µg g−1 Cd, 0.07–4.8 µg g−1; Hg, 0.02–0.23 µg g−1. It is suggested that tissue analysis of Enteromorpha is one of the most useful biological techniques available in estuaries for pin-pointing aqueous (as opposed to sediment) metal contamination, and also for providing data suitable for world-wide comparisons. Provisional values are given for concentrations corresponding to ‘moderate’ and ‘high’ pollution.