Sediments have a critical role in biogeochemical cycling, and benthic processes often support the base of aquatic food chains. The Anthropocene era has seen dramatic increases in the availability of nutrients, metals, and synthetic organics released into human-dominated watersheds, with evidence of global transport. Many of these chemicals are retained in sediments, which are the largest repository of chemicals globally. Sediments and their stored chemicals are not static with erosion and fluvial processes continually pumping sediments and their associated chemicals into depositional areas of streams, rivers, lakes, reservoirs, and coastal areas. These processes are likely to intensify as more extreme climate events occur in many parts of world. The US Army Corps of Engineers removes several hundred million cubic yards of dredged materials per year, with much of it simply being moved from channels to adjacent aquatic areas. This suggests that tens to hundreds of billions of cubic yards of sediments worldwide must be moved annually for navigation purposes, adding to the overall transport of sediments through our urban and agricultural landscapes. Thus the depositional and sorptive nature of fine-grained sediments has created hundreds of thousands, if not millions, of contaminated sites. Assessing the ecological impact and risk of these sediments has been challenging from both scientific and regulatory perspectives, and never before has it been more important to get it right.
THE PASTIn the United States, there was a period of rapid development of sediment assessment methods in the 1980s to mid-1990s, driven by regulatory attention and funding. One of the classic sediment toxicity methods papers, which guided further development, was Nebeker et al., published in 1984 [1]. This increased focus also occurred in Canada, Europe, Australia, and New Zealand in the 1990s. Several standardized toxicity test assays were developed by regulatory and standards-setting institutions, along with guidance on how to sample, handle, and characterize sediments [2][3][4][5]. A number of sediment quality guidelines based on equilibrium partitioning and empirical data were created [6,7]. Publications and presentations on chemically contaminated sediments dramatically increased. All of this activity was fueled by a host of regulatory mandates to assess and remediate contaminated sites. As is the case whenever there are potentially expensive regulatory drivers, a flurry of activity and some controversy followed regarding how to best address these mandates. Some of the controversy did not deal with the science, but rather policy issues, for example, whether we should call these newly devised values sediment quality standards, indicators, criteria, guidelines, benchmarks, alert, target, or quality levels, and so on. These labels represented differences that were subtle to many, yet huge to others. Many scientific points were widely discussed and published, such as the validity of the chemical-specific guidelines, optimal measurement endpoi...