Site of National Interest (SIN), Cengio (Savona), Liguria / Piemonte, Italy
Cengio and Saliceto (ACNA)
The ACNA works at Cengio, on a bend of the Bormida river at the border between Liguria and Piedmont: dynamite from 1882, then dyes and organic intermediates until 1999. About 1.5 million m³ of contaminated material have been permanently confined inside the site.
At a glance
- Status
- Contained
- Area
- 331 ha on land1
- Activity
- 1882–1999
- People affected
- 34,877 (2019)2
- Media
- soil, groundwater, surface water
- Kind of site
- chemical works, dyes, explosives, landfill
- Area. 331 ha is an ISPRA estimate from the geometry published in the Official Gazette: the official figure is under review at the Ministry (June 2024). Eni Rewind gives about 1,612 ha for the whole site, which includes the bed of the Bormida di Millesimo river (zones A, B and C). The plant covers 77 ha. Perimeter set by decree of 20 Oct 1999, redrawn by decree of 17 Oct 2024, which adds the Merlo area to zone A.
- People affected. Residents of the 32 site municipalities, 2019 census, from the SENTIERI Sixth Report.
Contaminants
Status
Contained
Of the plant's 77 ha: soil characterised and with an approved project on 100%, procedure closed on 56%; groundwater characterised and with an approved project on 100%, no procedure closed (ISPRA, June 2024). Permanent containment of zone A1 was built between 2018 and 2021; according to Eni Rewind (2025) the soil works are finished and groundwater is in post-works monitoring, with 45 extraction wells.
Story
A dynamite factory was set up at Cengio in 1882. From 1908 it made sulphuric acid, oleum and TNT; in 1925 the works were converted to dye production and in 1929 ACNA was formed, passing to Montecatini (1931), Montedison (1964), Enimont (1988) and Enichem (1991). Production ended in January 1999.
Documented in the soil are heavy metals, aromatic amines, halogenated aromatics, chlorobenzenes, hexachlorobenzene, phenols, nitrobenzenes, PAHs, PCBs, dioxins and naphthalene- and anthraquinone-sulphonic compounds; in groundwater, aluminium, arsenic, iron, manganese, lead and naphthalene sulphonates. The 1999 perimeter distinguishes a high-risk zone A (the plant, the Pian Rocchetta landfill and the Bormida river bed to just above Saliceto) and zones B and C along the river.
Under the 2000 programme agreement between ACNA, ministries, Regions and the government commissioner the plant was split into four zones: A1 (material deposit), A2 (plant area), A3 (floodplain) and A4 (Pian Rocchetta). The A1 lagoons, basins for saline effluent, were emptied; about 1.5 million m³ of material removed from zones A2, A3 and A4 was placed in A1, which was then capped. Along the river runs a 2,500 m cement-bentonite cut-off wall keyed into the marl, topped by a concrete wall about 5 m high on average.
Zone A4 was certified in 2010–2012 and A2 in 2010; for the floodplain areas an addendum to the project was approved in 2023. The EU infringement procedure, linked to the missing environmental impact assessment, was closed in June 2020 after a retrospective assessment. Since 2017 a protocol between the Regions, the ARPA agencies and Eni Rewind has monitored the Bormida's water: ARPA Piemonte reports that the attention thresholds have never been exceeded. Eni Rewind states it had spent 497 million euro by the end of 2025.
Timeline
- 1882The Cengio dynamite factory is set up.
- 1925Conversion to dye production; ACNA is formed in 1929.
- 1988The business passes to Enimont and the clean-up plan is started.
- 1998Law 426/1998 declares Cengio and Saliceto a Site of National Interest.
- 1999January: production ends. Perimeter set by decree of 20 Oct 1999.
- 2000Programme agreement: the plant is divided into zones A1–A4.
- 2006The government commissioner approves a clean-up project for each zone.
- 2010Zone A2 and the Ligurian part of Pian Rocchetta (A4) are certified; the Piedmontese part follows in 2012.
- 2020Retrospective impact assessment concluded in April; in June the European Commission closes the infringement procedure.
- 2024The decree of 17 October 2024 redraws the perimeter and adds the Merlo area.
Health
SENTIERI Sixth Report (2023; 32 municipalities of the valley, mortality 2013–2017, admissions 2014–2018): excess of circulatory diseases in both sexes and of digestive diseases in women; deficit of cancers in men. Among causes linked a priori to chemical plants, stomach cancer is in excess among women in both mortality and admissions, as seen in both sexes in earlier reports. In women, pleural mesothelioma: 6 deaths, SMR 270 (90% CI 140–522); malignant pleural tumours: 10 admitted, SHR 320 (90% CI 191–535), with no environmental asbestos source identified. All-cause admissions above expected at ages 0–19 and 20–29.
Remediation
- 2006excavationEmptying of the zone A1 lagoons and removal of about 1.5 million m³ of contaminated material from zones A2, A3 and A4.
- 2006containmentA 2,500 m cement-bentonite cut-off wall keyed into the marl, with a concrete wall above ground against Bormida floods.
- 2018cappingPermanent containment of zone A1, the deposit for the removed material (2018–2021).
- 2006pump and treatNetwork of 45 wells connected to the site's water treatment plant; 473,021 m³ treated in 2024.
Plants and fungi at this site
PhytoremediationField scale, pubbl. 2010
Polygonum aviculare
Survey of the spontaneous vegetation on hill A5, a waste dump of the works with multi-metal contamination. Plant species, biodiversity and health were related to soil metals in four areas of the hill and to accumulation in shoots and roots. It is a screening of native plants, not a clean-up trial.
Outcome Polygonum aviculare hyperaccumulated mercury in its shoots; several species accumulated more than two metals at once in both shoot and root.
MycoremediationField scale, pubbl. 2006
Solidago gigantea, Glomus spp.
Study of arbuscular mycorrhizal fungi in the roots of Solidago gigantea growing on the plant's waste hills, covered about 25 years earlier with uncontaminated soil to allow revegetation. Colonisation was examined by microscopy and the fungi identified by PCR-RFLP and 18S rDNA sequencing. The abstract speaks of heavy metals without listing them: the targets given here are those documented for the site.
Outcome Modest colonisation but normal fungal structures; 14 mycorrhizal fungal types, mostly Glomus, three found in all areas. The authors conclude that the soil cover restored a mycorrhizal community able to proliferate in still-contaminated soil.
Microbial bioremediationLaboratory, with soil from the site, pubbl. 2014
Methylobacterium populi
Fourteen bacterial strains able to grow on a mixture of xenobiotics as sole carbon source were isolated from soil of the former ACNA works. The best, Methylobacterium populi VP2, was also characterised for plant-growth-promoting activities. In an earlier study (2005) other authors had used the soil bacterial communities inside and outside the works as bioindicators, isolating strains that use 2,4-dichloroaniline.
Outcome M. populi VP2 degrades PAHs, produces indole-3-acetic acid and siderophores, solubilises phosphate, forms biofilm in the presence of phenanthrene and relieves phenanthrene stress in tomato seeds. No field test.
- Ventorino V. et al., Methylobacterium populi VP2: plant growth-promoting bacterium isolated from a highly polluted environment for PAH biodegradation, The Scientific World Journal 2014:931793, 2014
- Avidano L. et al., Characterization of soil health in an Italian polluted site by using microorganisms as bioindicators, Applied Soil Ecology 30(1):21-33, 2005
From the literature
Species that acted on one of this site's contaminants in at least one study. The list is automatic and takes no account of this site's soil, concentrations or climate.
Plants
- Agrostis capillarisCommon bentEvidence: field
- Cucurbita pepoZucchini, pumpkinPolychlorinated biphenylsDioxins and furansEvidence: field
- Festuca rubraRed fescueEvidence: field
- Medicago sativaAlfalfa, lucernePolychlorinated biphenylsPolycyclic aromatic hydrocarbonsEvidence: field
- Populus albaWhite poplarEvidence: field
- Pteris vittataChinese brake fernEvidence: field
Fungi
- Phanerochaete chrysosporiumPhenols and chlorophenolsPolychlorinated biphenylsDioxins and furansEvidence: field
- Trametes versicolorTurkey tailPhenols and chlorophenolsPolycyclic aromatic hydrocarbonsEvidence: field
- Funneliformis mosseaePolycyclic aromatic hydrocarbonsEvidence: greenhouse
- Rhizophagus irregularisEvidence: greenhouse
- Pisolithus albusEvidence: greenhouse
- Aspergillus nigerBlack mouldEvidence: laboratory
The rest are on the contaminant pages.
Nearby
SIN, Cogoleto e Arenzano (Genova), Liguria
Cogoleto-Stoppani chromium works
36 km
SIN, Serravalle Scrivia (AL), Piemonte
Serravalle Scrivia (former Ecolibarna)
64 km
- Petroleum hydrocarbons
- Mixed waste
Italy, Serravalle Scrivia (Alessandria), Piemonte
Serravalle Scrivia (land next to the KME works)
64 km
PhytoremediationMycoremediation
Italy, Spinetta Marengo, Alessandria, Piemonte
Spinetta Marengo (Solvay, now Syensqo, chemical plant)
66 km
- Per- and polyfluoroalkyl substances
- Chlorinated solvents (TCE, PCE, chloroform)
- Fluoride
Sources
- Siti contaminati di interesse nazionale (indicatore, dati a giugno 2024), ISPRA, 2024
- Riferimenti normativi per i SIN (aggiornamento 31 dicembre 2025), ISPRA, 2025
- Il SIN di Cengio e Saliceto (scheda del Dipartimento territoriale di Cuneo), ARPA Piemonte, 2024
- I nostri interventi ambientali a Cengio e Saliceto, Eni Rewind, 2025
- SENTIERI. Sesto Rapporto, Epidemiologia & Prevenzione 47(1-2) Suppl 1 (scheda Cengio e Saliceto, pp. 64-65; SENTIERI6_Siti_informazioni), Istituto Superiore di Sanità / Epidemiologia & Prevenzione, 2023
- Cengio (coordinate del comune), Wikipedia, 2026
Draft compiled from public sources, not yet reviewed.