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David Nightingale, CHMM Special Waste Associates CA 2015 Used Oil/HHW Training & Conference Session 5, Is Your HHW Program Convenient? April 9, 2015, Universal City

How convenient is convenient? Not well defined and agreed upon between policy-makers or individuals How many days per year is good enough? How many locations per 100k population is truly convenient? Difficult to determine what is good enough.

Removes subjectivity from consideration. If done well and agreed to Provides tangible goals, and Measures progress over time for a community, and Compares between programs serving different demographics

Traditional Recyclables are a large proportion of MSW stream and relatively easy to measure daily, weekly, and annually, e.g.: Recycling Programs: set out rates, pounds recycled per customer, % of waste diversion, tons diverted per year Composting programs can use same criteria Most other solid wastes can be evaluated with similar evaluation criteria, but NOT HHW

A household can easily store many years of HHW HHW is often generated because of an event Spring cleaning, death in the family, major remodeling project or maintenance Change of residence These generation events are typically not weekly, monthly or even annually, often multi-year Therefore, the appropriate performance measurement criteria must be based on a longer timeframe, a number of years

Total of all hazardous products sold Doesn t indicate how much product was used vs. waste Expensive retail sales data, may change over time Statistically significant survey of HHW in homes Very expensive, subjective regarding what may or may not be used prior to declared a waste by the homeowner Need to have a well defined definition of HHW and MSDS and other sources of HW would be challenging Develop an estimate of the average age of all HHW generated. Needs to be: broadly representative of HHW generation consistently purchased product that often becomes HHW

Most household cleaners, pesticides, used oil do not have dates of manufacture to easily determine their age. Architectural paint is an exception - Manufacturers have been required to date stamp their consumer paints due to VOC rules of the clean air act for many years, and many did so previously for Q.C. Paints are a traditional HHW and one of the largest proportions of HHW Paints might be representative of the average age of all HHW, but it certainly represents the 30-55% of the HHW that is paint. It might be a good HHW proxy.

From the Paint Product Stewardship Initiative State Paint as % of HHW California 34-43% Iowa 33% Washington 43.6% Wisconsin 30.9 56%

Performed a study of the age of paint delivered to five community HHW programs Hundreds of paint cans provided useable date codes. An age of paint profile was developed

Paint Age, Yrs Percentage of Paint Cans Paint Age, Yrs Percentage of Paint Cans 0 2.4 13 2.7 1 8.2 14 3.4 2 9.1 15 1.2 3 4.0 16 0.6 4 9.5 17 1.2 5 7.0 18 0 6 7.9 19 0.6 7 8.8 20 0.3 8 7.0 21 0.3 9 6.7 22 0.3 10 6.1 23 0.3 11 6.1 24 1.5 12 3.7 25+ 0.9

100% HHW Paint Age Cumulative Percentage 90% Cumulative Percent Distribution Paint Can Age, n-328 80% 70% 60% 50% 40% 30% 20% 10% 0% 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25+ Paint Age, Years

Average age of HHW paint is 7.4 years old, this can be considered the periodicity of the disposal cycle Greater than 50% of paint is seven years old or less Greater than 90% of paint is younger than 14 years old Less than 1% of HHW paints are over 25 years old

Assume HHW paint age is generally representative of the age of all HHW Use the average age of HHW paint to represent the average age of all HHW Assume the avg. age of HHW is a good estimate for the frequency of all HHW delivered Assume negligible effect of multiple-house loads due to offset from customers delivering HHW more than once per year

Use the annual participation rate of households in a services area in conjunction with the assumed average HHW age to calculate the annual effectiveness of any HHW collection program

In a national 2005 study of 25 HHW programs in the US it was found that the annual participation rate ranged between 2% to 24% of households in the program service territory, with a median of 7%. From: Comparison of Household Hazardous Waste Programs, Portland Regional Environmental Management (Portland Metro) by Cascadia Consulting Group, Fall 2005, p. 14

A similar study of seven selected California HHW programs in 2007 found annual participation rate between 2.1% and 13.1%. This variability is not only program/jurisdiction specific but varies by location within jurisdictional boundaries. Sonoma County, showed that for the entire county the participation rate was 8.3% However in three areas within the county the participation rate varied between 4% to 69%. The area of 69% participation rate was in the area surrounding the permanent collection facility and the outlying areas saw a steep drop in participating households who were served only by occasional collection events Sonoma HHW Program Benchmarking and Program Evaluation Study, Sweetser & Associates and Special Waste Associates, January 2007, accessed at: http://www.recyclenow.org/pdf/reports/sonoma_hhw_assessment_final_2007.pdf.

Assuming that an average HHW program can often achieve 7% annual household participation rates in the service area, multiply that by the estimated 7.4 years disposal cycle of HHW to arrive at an estimated effectiveness of 51.8% HHW participation rate for the disposal cycle.

Formula: PPR% X 7.4 = HHW Eff. % Where: PPR% is the Annual Participation Rate for the service area in a year 7.4 is the assumed disposal cycle for HHW, in years HHW Eff. % is the Estimated Percent Effectiveness of the HHW collection program in a year HHW Effectiveness calculation example: 7.0 % (avg. ann. participation) X 7.4 = 51.8 %

Using a constant multiplier and the higher end of participation rates can estimate effectiveness over 100% At about 14% annual participation rates you will calculate about 100% effectiveness

Effectiveness of HHW Collection HHW Collection Effectiveness 141% 148% 150% 140% 130% 118% 126%133% 120% 110% 96% 104%111% 100% 90% 74% 81%89% 80% 70% 52% 59%67% 60% 50% 40% 30% 37%44% 30% 20% 7% 15%22% 10% 0% 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 Annual HHW Participation Rate, % of Households

Jurisdiction Percent Participation Est. Effectiveness San Mateo County 2.7% 20% San Francisco 3.4% 25% San Bernardino 7.5% 55% Santa Cruz County 11.5% 85% Central Contra Costa Sanitary District 14.4% 107%

Increasing new customers => temporary increase in participation Actual average age of HHW non-paint is older than average HHW paints Customers bring in HHW more frequently than the average age of their HHW

Does not rely on difficult to estimate HHW generation or disposal rates Does not rely on methods that are not applicable to the generation patterns peculiar to HHW Simple calculation based on existing participation ratios which are easy to accurately measure

Allows comparisons between programs independent of demographics Allows tracking progress over time for the same collection program Provides a reasonable/rational goal or end point, 14% annual participation

David Nightingale, Principal Special Waste Associates www.specialwasteassoc.com dnight@cco.net