Dredging can cause increased suspended sediment concentrations (SSCs), light attenuation and sedimentation in marine communities. In order to determine the combined effects of dredging-related pressures on adult sponges, three species spanning different nutritional modes and morphologies were exposed to 5 treatment levels representing realistic dredging scenarios. Most sponges survived under low to moderate turbidity scenarios (SSCs of ≤ 33 mg L −1 , and a daily light integral of ≥0.5 mol photons m −2 d −1 ) for up to 28 d. However, under the highest turbidity scenario (76 mg L −1 , 0.1 mol photons m −2 d −1 ) there was 20% and 90% mortality of the phototrophic sponges Cliona orientalis and Carteriospongia foliascens respectively, and tissue regression in the heterotrophic Ianthella basta. All three sponge species exhibited mechanisms to effectively tolerate dredging-related pressures in the short term (e.g. oscula closure, mucus production and tissue regression), although reduced lipids and deterioration of sponge health suggest that longer term exposure to similar conditions is likely to result in higher mortality. These results suggest that the combination of high SSCs and low light availability can accelerate mortality, increasing the probability of biological effects, although there is considerable interspecies variability in how adult sponges respond to dredging pressures.Sediments released into the water column by natural resuspension, river runoff and human activities such as dredging pose a potential risk to sensitive ecosystems such as coral reefs, seagrass meadows and sponge gardens 1-4 . Sediments in suspension, or settling back out of suspension (i.e. sedimentation), can affect epi-benthic organisms in a number of ways, including clogging of the feeding and filtering mechanisms. Water turbidity (cloudiness) can also temporarily reduce or extinguish benthic light 4-6 . These stressors can act alone but more often in combination, making impact prediction particularly difficult. Sponges are sessile filter-feeding organisms that play important roles in marine ecosystems, including substrate consolidation, habitat provision, seawater filtration and bentho-pelagic energy transfer 7-9 . Despite their abundance and ecological importance, our understanding of how sponges respond to turbidity is still very basic 10, 11 . This knowledge gap poses significant challenges to their effective management, especially for anthropogenic turbidity-generating activities such as dredging, that can at least be subject to some regulation and control 12 .Most sponges obtain energy heterotrophically, by filtering seawater through an aquiferous system or internal canal network 13,14 . However, many sponges can also obtain energy autotrophically from photosymbionts, of which Cyanobacteria are the most common 15,16 . Some bioeroding sponge species also harbour dinoflagellates of the genus Symbiodinium as photosymbionts 17,18 . The photosymbionts can provide >50% of the energy requirement of the host for some tropical sponge spec...