Table 1.
Sediment Proxy | Description of proxy | Variable (s) proxy used to reconstruct | Delta stressor variable can inform on | References |
---|---|---|---|---|
Diatoms | Cosmopolitan fossilised microscopic algae with silica cell walls (frustules). The different morphologies of diatoms make them easy to identify. | • Community compositional and abundance changes can be used to reconstruct changes in nutrient enrichment, salinity, pH and the thermal/light structure of lakes (e.g. through shifts in benthic to pelagic species) • Lake and hydrological evolution reconstructions using community compositional changes and stable isotopes from their silica cell walls (e.g. δ18O) |
• Nutrient enrichment • Saline intrusion. • Natural to anthropogenic mediated hydrological alteration. • Industrial pollution • Natural to anthropogenic alterations to land-use • Natural to anthropogenic climate variability |
Leng and Barker (2006), Duong et al. (2019), Briddon et al. (2020) |
Algal pigments | The light absorbing compounds; chlorophylls and carotenoids of photosynthetic organisms | • Same as diatoms • Increased concentrations of cyanobacterial pigments could indicate the presence of cyanotoxins which are harmful to human and ecological health. |
• Same as diatoms • Public health impacts of cyanotoxins through inferred abundance changes in cyanobacterial pigments. |
Leavitt and Hodgson (2001), Waters et al. (2005) |
Zooplankton remains: Chironomids and Cladocerans | The different morphologies of fossilised head capsules of non-biting midges (Chironomidae) and the chitinous remains of water fleas (Cladocera) which include the carapace, headshield, and appendages. | • Chironomid assemblage changes have been used to reconstruct air temperature (using chironomid-temperature transfer function), trophic status and water depth. • Cladocera are not always well-preserved but one of the only fossil representatives from the pelagic zone. Compositional and abundance changes are used to infer changes in pH, trophic status and water depth. |
• Natural to anthropogenic climate change. • Natural to anthropogenic mediated hydrological alteration. • Nutrient enrichment |
Brooks (2006); Wojewódka et al. (2020). |
Ostracods | Fossilised calcium carbonate carapaces (shells) of the bi-valved crustacean which resemble water fleas. Ostracods are found in almost all aquatic habitats. | • Ratios of different geochemical elements and the stable isotope compositions of the ostracod shells can indicate changes to aquatic conditions • Presence/absence of species has been used to estimate past air temperature and salinity: The Mutual Ostracod Temperature Range (MOTR) and the Mutual Ostracod Salinity Range (MOSR). |
• Saline intrusion. • Hydrological alterations • Temperature variability • Industrial pollution (heavy metals) • Oxygenation (changes to oxygen within a water body could be driven by hydrological change/lake ontogeny or development over time/anoxia events etc.) |
Chivas et al. (1986), Gasse et al. (1987), Mischke et al. (2010) |
Foraminifera (forams) | Single-celled protists whose shells are built of calcium carbonate (calcareous) or from tiny grains of sand stuck together (agglutinate) | Species compositional and shell geochemistry changes used to reconstruct changes in multiple environmental conditions such as salinity and dominant elemental composition. | • Saline intrusion • Natural to anthropogenic hydrological alterations • Land-use change • Nutrient enrichment |
Scott and Medioli (1986), Benito et al. (2015) |
Pollen | Microscopic fossilised male fertilising agents from plants, trees, grasses and weeds. | • Climate change using compositional changes • Environment changes through compositional and abundance changes (e.g. increase in pollen from agricultural crops indicate human land-use modification) |
• Natural to anthropogenic climate variability • Natural to anthropogenic land-use change (e.g. conversion of mangrove forest to agriculture) • Natural to anthropogenic hydrological/water quality change |
Bennett and Willis (2001), Hofmann (2002) |
Plant macrofossils | Fossilised remains from vegetation that do not require microscopy to identify e.g. leaf, stem debris. | • Same as pollen | • Same as pollen | Birks (2001), Salgado et al. (2020) |
Sediment grain size | The size of the grains within a sediment sample provides information on the composition, source, transportation and deposition of the sediment. | • Used to identify frequency and magnitude of flood events/the speed of water which determines the deposition of the sediment and the connectivity to the surrounding watershed. | • Flooding events • Natural to anthropogenic climate variability • Natural to anthropogenic alterations to watershed morphometry/hydrology |
Tye and Coleman (1989), Liu et al. (2012), Chen et al. (2018) |
Spheroidal carbonaceous particles (SCPs) | Distinct component of black carbon formed by the combustion of fossil fuels (coal and oil) at high temperatures (>1000°C). | Fossil fuel combustion | • Industrialisation • Urbanisation |
Rose (2015), Engels et al. (2018) |
Geochemical analysis: heavy metals and minerals. | Identifying the elemental composition of sediment using techniques including XRF (X-ray fluorescence) | • Concentrations and ratios of different elements can infer erosion and land-use change. • Increased concentrations of heavy metals can indicate industrial, sewerage and mining activity. |
• Flooding events. • Natural to anthropogenic climate variability • Industrialisation (e.g. heavy metals) • Urbanisation • Mining activity |
Last and Smol (2002), Vonk et al. (2015) |
Stable isotopes from the sedimentary organic matter | Stable isotopes such as δ15N and δ13C can be used to determine the source of lake organic matter (e.g. terrestrial or allochthonous vs in-lake or autochthonous) and the trophic status of the lake. Measured using mass spectrometry. | • δ15N has been used to identify different N sources and processes of organic matter including sewerage and artificial fertiliser inputs, as well as N2-fixing cyanobacteria. • δ13C has been used to identify the productivity of lakes and inputs of terrestrial organic matter. |
• Nutrient enrichment • Natural to human-mediated land-use change (e.g. conversion of mangrove forest to agriculture) |
Meyers and Teranes (2001), Wengrat et al. (2018) |
Sedimentation rates | Determined by measuring the radioactive nuclide signatures in the sediment such as 210Pb/137Cs etc. | • Changes to sedimentation rates can be used to reconstruct changes in sources of sediment and their transport. The deposition of sediments within a lake can also tell us about the thermal structure of the water column and its chemistry, its bathymetry and hydrological regime. | • Flooding events • Natural to human-mediated land-use change • Natural to anthropogenic climate variability • Natural to anthropogenic alterations to watershed morphometry/hydrology • Nutrient enrichment • Industrialisation • Urbanisation |
Gell et al. (2009), Xu et al. (2017). |