Despite its shortcomings, the OSHA lead standard caused nearly revolutionary improvements for workers in lead industries. Once OSHA started rulemaking, it was all downhill to a protective standard that survived legal challenge by industry. Partly as a result, the industry strategy since has been to prevent OSHA from starting rulemaking on chemicals. BASIS FOR THE CURRENT OSHA STANDARDS The explanation of the 1978 standard shows that OSHA sought to identify a body burden of lead—as indicated by LIB measurements—associated with adverse health effects, then sought to identify an LIA level that would keep the body burden below the LIB level. Workers whose LIB reached a dangerous range, or who suffered signs of illness, would be pulled out of exposure according to MRP-MPR, to be returned when the level decreased. This yo-yo process was standard industry practice at the time. The preamble to the lead standard states that LIB >40 µg/dl was associated with a risk, but the MRP-MPR provisions only require removal with a three-test moving average >50 µg/dl, with return permitted when the level got below 40 µg/dl. Today these values would be considered high, if not alarming, but in the middle 1970s about 70 percent of LIB measurements among battery plant workers (I had the data) were >40 µg/dl. Next, OSHA had to identify an LIA limit consistent with the LIB goals. There were no robust direct observations (such as multiple air samples, with attendant variability, and blood samples on a representative number of workers). So a pharmacokinetic model was used, which projected that 30 percent of workers would suffer LIB results >40 µg/dl, 6 percent between 40–50, and 1 percent >60 at an LIA of 50 µg/m3. The explanation provided in the lead standard preamble states, “While OSHA agrees with the goal that blood lead levels should be kept below 50 µg/100 g where possible, and in fact preferably below 40 µg/100 g, the levels required to achieve the latter value are clearly infeasible in the foreseeable future.” The OSHA LIA limit of 50 µg/m3 (total dust) is still as strict as any in the world. But we are now beyond OSHA’s “foreseeable future,” and it’s time to reassess both health and feasibility. Generally, lead exposure has been radically reduced. The median LIB result for adults in the U.S. is about 1 µg/dl; in 1976, my LIB was 25 µg/dl (confirmed by the Chrysler IH lab) with no occupational lead exposure beyond some battery-plant walkthroughs. EPA has reduced the National Ambient Air Quality Standard for lead to 0.15 µg/m3 (from 1.5 µg/m3). California EPA recently reassessed LIA-LIB associations; their model predicts a median LIB of 20 µg/dl at an LIA of 18 µg/m3, with 5 percent of results >43 µg/dl. An estimate based on surface contamination was shelved. For a median LIB of 10 µg/dl, the LIA would be 7 µg/m3. For IHs overseeing a lead removal project, the goal should be to apply all feasible controls to operations in the purgatory between the 1978 standard and current health criteria. First, we have to understand (and resist) complexity in exposure assessment. “Inhalable” (<50 µ) particle measurements are as much as three times “total” (closed-face cassette) results side by side, so there’s invisible exposure going to the gut, while only a fraction of the total is going to the alveolar surface. We could also invoke the chemical state of lead to suggest more complex and expensive assessments, and looser evaluation criteria (which have evolved for lead oxide dust and fume). Second, any LIB >10 µg/dl in a group of similarly exposed workers should trigger assessment of sources of exposure for the whole group, not just the worker with the elevation. Variation in absorption and storage means that the LIB is an imperfect measure of body burden. Precautions should be taken for all similarly exposed workers. Third, protections should be based on exposure. We should not be yo-yoing workers in and out based on their LIB. Regarding a possible PEL update, a question of priority still remains. Should OSHA attempt to improve a deficient but semi-modern standard, or focus on substances for which exposure limits are mired in the deeper past?
- California EPA: “Estimating Workplace Air and Worker Blood Lead Concentration using an Updated Physiologically-based Pharmacokinetic (PBPK) Model” (PDF, Oct. 2013).
- Cornell University Law School: UAW v. Johnson Controls (March 1991).
- OSHA: Regulations (Preambles to Final Rules).
- National Toxicology Program: “NTP Monograph: Health Effects of Low-level Lead” (PDF, June 2012).