Asbestos Atlas›Narratives›Long Beach

Facility evidence class — Tier 1 of 3 · Peer-Reviewed Cohort

Strongest facility evidence class: peer-reviewed cohort evidence; read the source's population and yard-attribution limits.

Long Beach Naval Shipyard

Long Beach, California · Est. 1940 · U.S. Navy civilian and military workforce · Closed 1997 · EPA Superfund Site CA1170090483

Long Beach Naval Shipyard operated from 1940 to 1997, employing a peak workforce of 16,091 during World War II and approximately 17,000 at closure. A 1979 chest x-ray survey of 6,640 employees — 88.6% of the entire workforce — found that 16% had asbestos-related radiographic abnormalities, rising to 38% among older workers and 37% among those with 22–26 years of service. A 1964 industrial hygiene paper by a yard hygienist documents the specific amosite-containing products used in shipboard insulation work, providing the product-level evidence that explains the high radiographic prevalence.

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Verified Evidence Records
Facility evidence class — Tier 1 of 3 · Peer-Reviewed Cohort
Facility Evidence Class
16%
Workforce Radiographic Prevalence
6,640
Workers Surveyed (Felton 1979)

Bottom Line Up Front

A 1979 chest x-ray survey of 6,640 Long Beach Naval Shipyard employees (88.6% of the workforce) found asbestos-related radiographic abnormalities in 16.0% of workers — rising to 38.2% among those aged 65+ and 37.0% among those with 22–26 years of service (Felton 1979, PMID 294186). A 1985 study found that 11.3% of wives and 7.6% of sons of Los Angeles County shipyard workers showed radiographic signs of pulmonary asbestos disease from take-home contamination (Kilburn 1985, PMID 4003623). A 1964 industrial hygiene paper by a Long Beach yard hygienist documents the specific products: 100% amosite blankets and 85% magnesia/15% amosite blocks accounted for approximately 88% of insulator time aboard ship (Marr 1964). Four independent records — two peer-reviewed radiographic studies, one product documentation paper, and an EPA Superfund ROD — converge on the same conclusion: Long Beach Naval Shipyard was a high-intensity asbestos exposure site where disease affected one in six active workers and spread to their households.

Primary Source — Felton et al. (1979)

Radiographic Survey — 6,640 Workers, 16% Prevalence

The Felton 1979 study is the foundational primary source for Long Beach's Facility evidence class — Tier 1 of 3classification. It is one of the largest facility-specific radiographic surveys conducted at any U.S. naval shipyard, covering 88.6% of the entire workforce at a single point in time. The 16% prevalence figure — rising to 38% among older workers — is among the highest documented at any U.S. government shipyard.

Key Findings

  • ▸16.0% of the 6,640 employees surveyed (1,061 workers) had asbestos-related radiographic abnormalities — pleural plaques, pleural thickening, or interstitial fibrosis consistent with asbestosis.
  • ▸Prevalence rose sharply with age: 38.2% of workers aged 65 or older showed radiographic abnormalities.
  • ▸Prevalence rose sharply with service length: 37.0% of workers with 22–26 years of service showed radiographic abnormalities.
  • ▸The survey covered 88.6% of the entire workforce — one of the highest participation rates in any shipyard radiographic study — making the 16% prevalence figure highly representative.
  • ▸The study was conducted at a time when many workers were still employed, meaning the true lifetime prevalence in the cohort would be higher due to the latency of asbestos disease.

Methodology

Cross-sectional chest x-ray survey of 6,640 Long Beach Naval Shipyard employees, representing 88.6% of the total workforce. Radiographs were read using the ILO/UC classification system for pneumoconiosis. Prevalence of asbestos-related abnormalities was stratified by age, service length, and trade. The study was conducted in 1979 as part of a Navy-wide occupational health screening program.

Limitations

Radiographic prevalence study — it documents the burden of asbestos disease in the workforce at a single point in time, but does not report mortality rates or mesothelioma incidence. Workers who had already died from asbestos-related disease before 1979 are not captured. The true lifetime disease burden in the cohort is therefore higher than the 16% prevalence figure.

Why This Study Matters

A 16% radiographic abnormality rate across 88.6% of the workforce is one of the highest facility-specific asbestos disease prevalence figures documented at any U.S. naval shipyard. The age and service-length gradients (rising to 38% and 37% respectively) are consistent with a dose-response relationship and confirm that the exposure was occupational rather than incidental. The Felton study is the primary source for Long Beach's Facility evidence class — Tier 1 of 3 classification.

PubMed PMID 294186 ↗Radiographic prevalence study, 1979
Felton JS, et al. Asbestos-related disease in employees of a naval shipyard. J Occup Med. 1979;21(3):168–173. PMID 294186.

Product Documentation — Marr (1964)

Asbestos Products at Long Beach — Named by a Yard Industrial Hygienist

The Marr 1964 paper is one of the few primary sources that names specific asbestos products and their application methods at a named naval shipyard. Written by a Long Beach Naval Shipyard industrial hygienist, it documents the insulation materials used in shipboard steam power plant overhaul — the primary asbestos exposure pathway for the workers surveyed by Felton in 1979.

Key Findings

  • ▸100% amosite asbestos blankets were used for shipboard insulation in steam power plants until approximately 1962.
  • ▸85% magnesia + 15% amosite asbestos blocks and pipe sections accounted for approximately 88% of insulator time aboard ship.
  • ▸Workers applied 85% magnesia plaster and wrapped finished insulation with asbestos cloth — creating multiple simultaneous exposure pathways.
  • ▸The paper is authored by a Long Beach Naval Shipyard industrial hygienist and documents the specific products and application methods used at the yard.

Why This Source Matters

The Marr 1964 paper is one of the few primary sources that names specific asbestos products and their application methods at a named naval shipyard. It provides the product-level evidence that explains the 16% radiographic prevalence found by Felton 1979: workers who spent 88% of their time handling amosite-containing insulation blocks and blankets were exposed to high fiber concentrations throughout their careers.

Marr 1964 — Full Text ↗Am Ind Hyg Assoc J, 1964
Marr WT. Asbestos exposure during naval vessel overhaul. Am Ind Hyg Assoc J. 1964. (Long Beach Naval Shipyard affiliation).

Take-Home Exposure — Kilburn et al. (1985)

Asbestos Disease in Family Contacts — 11.3% of Wives, 7.6% of Sons

The Kilburn 1985 study extends the documented harm beyond the workforce to their households. Take-home asbestos disease — caused by fibers carried home on work clothing — is a recognized marker of extreme occupational exposure. The finding that more than one in ten wives of shipyard workers showed radiographic signs of pulmonary asbestos disease corroborates the Felton 1979 prevalence data and confirms that exposure levels at Los Angeles County shipyards were severe.

Key Findings

  • ▸11.3% of wives of shipyard workers showed radiological signs of pulmonary asbestos disease — from household (take-home) asbestos contamination carried home on work clothes.
  • ▸7.6% of sons of shipyard workers showed radiological signs of pulmonary asbestos disease from the same take-home pathway.
  • ▸Comparable radiographic signs were not found in control groups without shipyard family connections.
  • ▸The study demonstrates that asbestos exposure at Los Angeles County shipyards — including Long Beach — was severe enough to cause disease in household contacts who never set foot in the yard.

Methodology

Radiographic survey of 274 wives and 79 sons of Los Angeles County shipyard workers with at least 20 years elapsed since initial hire. Chest x-rays were read using the ILO classification system. Control groups without shipyard family connections were compared. The study covers Los Angeles County shipyards collectively and does not isolate Long Beach Naval Shipyard specifically.

Limitations

The study names 'shipyards in Los Angeles County' collectively — it does not isolate Long Beach Naval Shipyard specifically. A correction note was published in December 1985 (Am J Public Health 75(12):1397). The claimed WWII period is unsupported; the study is a 1980s radiographic survey with ≥20-year latency from hire. Results are attributable to the Long Beach yard as the dominant naval facility in the region but cannot be assigned exclusively to it.

Why This Study Matters

Take-home asbestos disease in family members is a recognized marker of extreme occupational exposure — it requires fiber concentrations high enough to contaminate work clothing at levels sufficient to cause disease in people with only indirect contact. The Kilburn 1985 findings corroborate the Felton 1979 prevalence data and extend the documented harm beyond the workforce to their households.

PubMed PMID 4003623 ↗Am J Public Health, 1985
Kilburn KH, Lilis R, Anderson HA, et al. Asbestos disease in family contacts of shipyard workers. Am J Public Health. 1985;75(6):615–617. PMID 4003623. DOI 10.2105/AJPH.75.6.615.

Environmental Record — Navy ROD (2005)

Record of Decision — IR Site 9 · EPA ID CA1170090483

The Navy's Record of Decision for IR Site 9 (Building 129 spills) is the primary environmental record for the former Long Beach Naval Complex. It confirms the yard's identity, scale, and operational history as a major naval repair and overhaul facility, and provides the EPA Superfund listing that independently corroborates the yard's documented contamination footprint.

Key Findings

  • ▸The Record of Decision for IR Site 9 (Building 129 spills) documents the federal remediation plan for solvent contamination (PCE/TCE/vinyl chloride) at the former Long Beach Naval Complex.
  • ▸The EPA Superfund listing (ID CA1170090483) confirms that the yard's historical operations left a documented environmental contamination footprint.
  • ▸The ROD is the primary environmental record for the named yard, confirming its identity and operational history as a major naval repair and overhaul facility.
  • ▸The contamination addressed in the ROD is solvent-based rather than asbestos-specific; it is included as the primary environmental record for the facility, not as an asbestos-disease document.

Why This Record Matters

The Navy ROD and EPA Superfund listing provide independent federal regulatory confirmation of the yard's identity, scale, and operational history. Combined with the Felton 1979 and Kilburn 1985 radiographic studies, the three records converge on a consistent picture: a large naval facility where asbestos exposure was severe enough to cause disease in 16% of the active workforce and in the household contacts of workers.

Navy ROD — IR Site 9 ↗EPA Superfund ID CA1170090483 · 2005
Dept. of the Navy. Record of Decision/Remedial Action Plan, IR Site 9, Former Long Beach Naval Complex (August 2005). LBNC IR Site 9 ROD/RAP.

Documented Asbestos Products

Named Products from Primary Sources

The Marr 1964 paper is one of the few primary sources that names specific asbestos products at a named naval shipyard. The following products are documented by a Long Beach Naval Shipyard industrial hygienist:

100% Amosite Asbestos Blankets

Shipboard insulation; steam power plants; used until ~1962

85% Magnesia / 15% Amosite Blocks & Pipe Sections

~88% of insulator time aboard ship; primary insulation material

85% Magnesia Plaster

Applied over amosite blocks as finishing layer

Asbestos Cloth Wrap

Final wrap over finished insulation on pipe and boiler surfaces

Further reading: asbestos exposure at Long Beach Naval Shipyard — WikiMesothelioma.com

About the Authors

Paul Danziger

Founding Partner, Danziger & De Llano, LLP

Paul Danziger has represented mesothelioma patients and their families for over 25 years. He holds a J.D. from Northwestern University Pritzker School of Law and has secured hundreds of millions in verdicts and settlements for shipyard workers, veterans, and industrial tradespeople exposed to asbestos. His practice focuses exclusively on asbestos-related disease litigation.

Rod De Llano

Founding Partner, Danziger & De Llano, LLP

Rod De Llano co-founded Danziger & De Llano to advocate for workers harmed by corporate asbestos negligence. With a career spanning over two decades in toxic tort litigation, he has developed deep expertise in shipyard exposure patterns, product identification, and occupational disease causation. He represents clients nationwide in mesothelioma and asbestosis claims.

Danziger & De Llano, LLP funds the Asbestos Atlas as a public-interest research project. The dataset is published under CC BY 4.0 and sourced exclusively from primary records (PubMed, NIOSH, EPA, NARA). No law-firm marketing material is used as a data source. See Methodology for the full circularity firewall protocol.