## 1. Introduction

Over the last few decades, U.S. agriculture has benefited from rapid increases in farm productivity (Wang et al., 2015), driven primarily by technological innovations and improved farm management. Higher productivity has contributed to increased profitability and competitiveness of U.S. farmers in a global marketplace. Fertilizer use has helped maintain or enhance soil productivity; pesticides have contributed to reducing the adverse effects of pest damages; and biotechnology has joined with traditional breeding methods to improve the desired genetic characteristics of seeds in agriculture. In particular, since its inception of commercialization in 1996, the world has seen a rapid growth in genetically modified (GM) crops planted in both developed and developing countries. It has generated much interest in evaluating the effects of biotechnology on agriculture (e.g., Bustos, Caprettini, and Ponticelli, 2016; Carpenter, 2010; Klümper and Qaim, 2014; Perry, Moschini, and Hennessy, 2016). The United States is currently the leading adopter of GM staple crops, with adoption rates exceeding 90% each for GM soybean, cotton, and corn (Fernandez-Cornejo et al., 2014; USDA, 2017a).

This study seeks to develop a greater understanding of the implications of GM technology adoption on the farm demand for inputs. Of special interest is evaluating the distinct effects between two aspects of GM technology: Bt technology (relying on gene transfer from *Bacillus thuringiensis*), which helps control the pest population for corn and cotton; and herbicide tolerance (HT) technology, which helps control weeds for corn, soybean, and cotton (Fernandez-Cornejo et al., 2012, 2014; Gardner, Nehring, and Nelson, 2009; Perry et al., 2016; Xu et al., 2013). In general, GM seeds can have a considerable impact on pesticide use, but the impact may be different for insecticide use versus herbicide use. GM corn with corn borer and rootworm insect resistance can lead to lower insecticide applications. Yet the GM crop with HT traits may lead to more or lower herbicide applications depending on farm practices. Perry, Moschini, and Hennessy (2016) found that HT traits and conservation tillage are complements. Biotech traits may also act as a substitute for crop rotation to some extent (Chavas, Shi, and Lauer, 2014). In the past, farmers rotated corn and soybeans to keep targeted insects from gaining a foothold on specific plots of farmland. However, in the GM seed era, each plant is protected and insects have limited ability to survive in GM fields; thus, farmers adopting GM may use less crop rotation in planting. Moving away from flexible rotation strategies could alter the demand elasticities for inputs in ways that affect the exercise of market power by agricultural input firms and the pricing of farm inputs. This study examines these issues, thus shedding new light on the economic effects of biotechnology on U.S. agriculture.

Our analysis relies on the estimation of a cost function and the corresponding input cost shares conditional on input prices, intermediate output, and technology. Such an approach provides the information needed for our investigation, including the evaluation of technological change, the temporal effects of biotechnology, and the evolving nature of price elasticities of input demands. However, it faces a significant challenge: agricultural production is risky as factors such as drought and pest damages can have unpredictable effects on farm output. Yet farm inputs are typically chosen ex ante—that is, before risky shocks become realized (e.g., fertilizer use is decided before weather conditions are known). For risk-averse farmers, it implies that farm input demands must depend on the distribution of risky output (Pope and Chavas, 1994).^{1} It means that, unlike standard cost minimization, input demands cannot depend on actual output as it is unobserved ex ante (LaFrance and Pope, 2010). This study deals with this issue by relying on a cost function that depends not on final output but rather on intermediate output. LaFrance and Pope (2010) showed that the validity of standard cost minimization can be restored under a weakly separable production function. Following similar arguments, we assume a weakly separable production function and rely on a cost function conditional on intermediate output. In this context, standard cost minimization remains valid under production uncertainty and risk aversion, thus providing the conceptual framework for our analysis.

The analysis is applied to U.S. agriculture, relying on two data sets: time series data on farm inputs and output at the U.S. level over the period 1960–2013 and time series data from nine Corn Belt states over the period 1960–2004. The data on Corn Belt states are of interest as the Corn Belt experienced the largest impact of GM technology. Unfortunately, the state-level data end in 2004 (when the U.S. Department of Agriculture [USDA] stopped collecting data on farm labor at the state level). The U.S.-level data have the advantage of covering the post-2004 period, when GM adoption became widespread for corn, soybean, and cotton. The analysis involves the estimation of demands for six inputs: (1) labor, (2) energy, (3) fertilizer, (4) herbicides, (5) insecticides, and (6) other inputs. The distinction between herbicide and insecticide is of special interest for two reasons. First, distinguishing between herbicide and insecticide is apparently new in the analysis of agricultural productivity and technological change bias. Second, studying the linkages between herbicide demand, pesticide demand, and biotechnology adoption is of significant interest to farmers, researchers, and policy makers (as biotechnology generates new ways to manage weed and pest control).

Our investigation documents how technology has affected farm productivity and input demands. Although the rapid productivity growth has been a common feature of U.S. agriculture over the last few decades, our analysis examines the changing patterns of productivity under biotechnology. It finds that biotechnology has contributed to speeding up productivity growth in the Corn Belt, but not at the U.S. level. It also documents the evolving biases in technological change in agriculture. We find that Bt and HT technologies have different impacts on farm input demands. Bt technology has increased the bias in favor of fertilizer use. By reducing pest damages, this finding indicates that Bt technology makes it easier for the plant to benefit from fertilizer applications. HT technology, however, tends to be fertilizer saving. The fertilizer-saving bias may reflect that improved weed control increases the availability of soil nutrients to the plant, thus reducing the need for fertilizer applications. Finally, we find evidence that farm demands for fertilizer, herbicide, and insecticide have become more inelastic after the GM inception (i.e., less responsive to prices). Thus, although biotechnology has contributed to technological progress in agriculture, GM adoption has also been associated with more restricted choices and a lower ability of farmers to adjust to changing market conditions.

The rest of the article is organized as follows: Section 2 presents our model of input choice, motivating our cost function approach. Relying on a translog cost specification, Section 3 presents an application to U.S. agriculture. The econometric results are presented in Section 4. The economic implications of our analysis are examined in Section 5. Finally, Section 6 concludes.

## 2. A Model of Input Choice

This section presents the conceptual approach to our analysis. Consider a production process involving inputs ${\bm{x}} \in \mathbb{R}_ + ^n$ and capital *K* in producing output *z* under production uncertainty. The production function *g*(*x*, *t*, *K*, *u*) represents the largest possible output *z* that can be obtained using factors (*x*, *K*) under technology *t* in the presence of a stochastic shock *u* (e.g., weather event and/or infestation shock).^{2} As discussed in the introduction, farm input decisions are often made before stochastic production shocks are known, implying that input demand cannot depend on actual output (as in standard cost minimization; see LaFrance and Pope, 2010). Instead, input demand would depend on the perceived distribution of final output (e.g., Pope and Chavas, 1994). Rather than trying to measure this distribution, our study uses a modified approach that can reinstate the validity of standard cost minimization. Following LaFrance and Pope (2010), assuming a weakly separable production function provides the proper analytical framework. In our analysis, we propose to distinguish between actual final output (that is subject to production shocks) and an “intermediate output” (that is immune to uncertainty). In this context, we assume that the production function is weakly separable and can be decomposed into two stages: in stage 1, under technology *t*, inputs *x* are used to produce intermediate output *y* = *f*(*x*, *t*); in stage 2, the intermediate output *y* is combined with capital *K* under stochastic shock *u* to produce output *z* = *g* _{0}(*f*(*x*, *t*), *K*, *u*) = *g*(*x*, *t*, *K*, *u*). Note that this specification restricts technology *t* to affect only the intermediate output *y* in the first stage of the production process. It allows for arbitrary possibilities of substitution among inputs *x* and imposes no restrictions on the effects of technology *t* on input productivity, nor on the effects of (*K*, *u*) on final output *z*.

We consider the case where the production process takes place over time, and input choices *x* are made before the stochastic shock *u* is observed (e.g., inputs are chosen at the beginning of the growing season before weather conditions are known). Denote by ${\bm{r}} \in \mathbb{R}_{ + + }^n$ the vector of prices for inputs *x*. Under the production function *z* = *g* _{0}(*K*, *u*, *y*) where *y* = *f*(*x*, *t*), and conditional on intermediate output *y*, a rational decision maker will always choose inputs *x* so as to minimize cost ${\rm{Mi}}{{\rm{n}}_{{\bm{x}} \in \mathbb{R}_ + ^n}}\ \{ {{\bm{r}} \cdot {\bm{x}}:\ y = f( {{\bm{x}},{\bm{t}}} )} \}$. Note this result holds under general conditions as long as the decision maker has preferences that are nonsatiated in income. Indeed, it holds under production risk (represented here by the stochastic shock *u*), under output price risk, and under farmers’ risk aversion. To see this, conditional on *y*, cost minimizing input choices would always stochastically dominate any other feasible input choice.

On that basis, conditional on (*r*, *y*, *t*), our analysis proceeds assuming cost minimizing behavior where inputs *x* are chosen as follows:

where *C*(*r*, *y*, *t*) is the indirect cost function, and *x*^{c}(*r*, *y*, *t*) denotes the cost minimizing input demand functions. Conditional on intermediate output *y*, cost minimization in equation (1) holds because, under weak separability, the marginal rates of substitution among inputs *x* are independent of the stochastic shocks *u*. In general, the cost function *C*(*r*, *y*, *t*) in equation (1) is linear, homogeneous, and concave in prices *r*. When the cost function *C*(*r*, *y*, *t*) is differentiable, it satisfies Shephard's lemma, where $\frac{{\partial C( {{\bm{r}},y,{\bm{t}}} )}}{{\partial {r_i}}} = {\bm{x}}_i^c( {{\bm{r}},y,{\bm{t}}} )$, *i* = 1, . . ., *n*. Shephard's lemma can be alternatively written as

where ${w_i}( {{\bm{r}},y,{\bm{t}}} ) = \frac{{{r_i}\ x_i^c( {{\bm{r}},y,{\bm{t}}} )}}{{C( {{\bm{r}},y,{\bm{t}}} )}}$ is the cost share for the *i*th input. Our empirical analysis will rely on the specification and estimation of the cost function *C*(*r*, *y*, *t*) given in equation (1) and the cost share equations *w*^{c}_{i}(*r*, *y*, *t*) given in equation (2).

The cost minimization problem in equation (1) has well-known implications for input demands (e.g., Chambers, 1988). From the Euler theorem, the linear homogeneity of *C*(*r*, *y*, *t*) in *r* implies the homogeneity conditions

We are interested in evaluating the effects of input prices *r*, intermediate output *y*, and technology *t* on input demand. First, the effects of prices can be measured by the price elasticities of input demands $\frac{{\partial \ln ( {x_i^c} )}}{{\partial \ {\rm{ln}}( {{r_j}} )}}$ for *i*, *j* = 1, . . . ., *n*. Following Berndt and Wood (1975), these demand elasticities satisfy

where ${\delta _{ij}} = \{ \scriptsize{\begin{array}{@{}*{1}{c}@{}} 1\\ 0 \end{array}} \}$ when $i\{ \scriptsize{\begin{array}{@{}*{1}{c}@{}} = \\ \ne \end{array}} \}j.$ Second, from Chambers (1988), economies of size evaluated at point (*r*, *y*, *t*) can be written as

where $ES( {{\bm{r}},y,{\bm{t}}} )\{ \scriptsize{\begin{array}{@{}*{1}{c}@{}} > \\ = \\ < \end{array}} \}\ 1$ corresponds to $\{ \scriptsize{\begin{array}{@{}*{1}{c}@{}} {{\rm{increasing}}}\\ {{\rm{constant}}}\\ {{\rm{decreasing}}} \end{array}} \}$ return to size in the neighborhood of (*r*, *y*, *t*). Third, the rate of technological change evaluated at point (*r*, *y*, *t*) can be written as

where *RTC*(*r*, *y*, *t*) measures the proportional change in output because of technological change in the neighborhood of (*r*, *y*, *t*). Finally, from Binswanger (1974), the nature of technological change can be expressed in terms of the bias in technological change

Technological change is said to be Hicks neutral when *B*_{i}(*r*, *y*, *t*) = 0 for all *i* and all (*r*, *y*, *t*). It is Hicks-biased toward the *i*th factor (or *i*th factor using) when *B*_{i}(*r*, *y*, *t*) > 0, and it is Hicks-biased against the *i*th factor (or *i*th factor saving) when *B*_{i}(*r*, *y*, *t*) < 0. Thus, departures from Hicks-neutral technological change correspond to situations where technological change affects the cost share of some inputs. Such effects are relevant in the evaluation of the “induced innovation” hypothesis (e.g., Binswanger, 1974). Under induced innovations, technological change responds to relative scarcity: new technology would develop to reduce the demand for inputs that are becoming more expensive (i.e., leading to “input saving” bias) and to increase the demand for inputs that are becoming cheaper (i.e., leading to “input using” bias).

## 3. An Application to U.S. Agriculture

In this section, we apply the model discussed previously to U.S. agriculture using a translog cost specification. Our investigation involves six inputs: (1) labor, (2) energy, (3) fertilizer, (4) herbicides, (5) insecticides, and (6) other inputs.^{3} Given our focus on biotechnology, we include three variables for technology: a time trend defined as *t* = *year* − 2000, which captures long-term technical change, and the variables *Bt*(*t*) and *HT*(*t*), which measure biotechnology adoption at time *t* (“insect resistance” for *Bt*(*t*) and “herbicide tolerance” for *HT*(*t*)). Thus, conditional on (*r*, *y*, *t*), we consider a translog specification for the cost function *C*(*r*, *y*, *t*) of the form

where (*a*, δ, *b*, *d*, *e*) are parameters, *a* = (*a* _{1}, *a* _{2}, . . ., *a* _{6}), *b* = (*b* _{1}, *b* _{2}, . . ., *b* _{6}), *d* = (*d* _{1}, *d* _{2}, . . ., *d* _{6}), and *e* = (*e* _{1}, *e* _{2}, . . ., *e* _{6}), satisfying the symmetry conditions *a*_{ij} = *a*_{ji} for *i* ≠ *j*, and ε_{0} is an error term with mean zero. The specification (equation 7a) is flexible in the sense that it does not impose a priori restrictions on the elasticities of substitution among inputs (Diewert and Wales, 1987). The variables *Bt*(*t*) and *HT*(*t*) in equation (7a) identify explicitly the role of biotechnology. From equation (5), the parameter δ captures returns to scale, with $\delta \ \{ \scriptsize{\begin{array}{@{}*{1}{c}@{}} < \\ = \\ > \end{array}} \}\ 1$ under $\{ \scriptsize{\begin{array}{@{}*{1}{c}@{}} {{\rm{increasing}}}\\ {{\rm{constant}}}\\ {{\rm{decrasing}}} \end{array}} \}$ returns to scale.

Using Shephard's lemma in equation (2), the cost share of the *i*th factor associated with equation (7a) is

where ε_{i} is an error term with mean zero, *E*(ε_{i}) = 0, and variance/covariance *E*(ε_{i} · ε_{j}) = σ_{ij} for *i*, *j* = 0, . . ., 6. Applied to equations (7a) and (7b), the homogeneity restrictions in equation (3) are as follows: $\mathop \sum _{i = 1}^6 {a_i} = 1$, $\mathop \sum _{i = 1}^6 {a_{ij}} = 0$ for all *j*, and $\mathop \sum _{i = 1}^6 {b_i} = \mathop \sum _{i = 1}^n {d_i} = \mathop \sum _{i = 1}^6 {e_i} = 0$. Equations (7a) and (7b) are a system of seven stochastic equations that can be estimated econometrically. Noting that $\mathop \sum _{i = 1}^6 {w_i} = 1$ implies that knowing five cost shares is equivalent to knowing the sixth one. It means that we drop one share equation without a loss of information. When using maximum likelihood estimation, the econometric results are invariant to the equation dropped (Barten, 1969). On that basis, we proceed estimating six equations: the cost equation (7a) along with five cost share equations in (7b).

Our empirical analysis relies on farm input and output data reported by the USDA's Economic Research Service (ERS). We examine agricultural productivity in the United States in general and in the Corn Belt states because GM adoption is significantly concentrated in the staple crops such as corn and soybean. The investigation will evaluate the rate and nature of technological change and its implications for the structure of input demand. Our sample information involves annual data starting in 1960. At the U.S. level, the data cover the period 1960–2013. However, USDA-ERS stopped reporting state-level data after 2004. Thus, our state-level analysis covers the period 1960–2004. Our analysis focuses on nine states in the Corn Belt: Illinois (IL), Iowa (IA), Indiana (IN), Michigan (MI), Minnesota (MN), Missouri (MO), Nebraska (NE), Ohio (OH), and Wisconsin (WI). We chose the Corn Belt for two reasons: (1) corn and soybean are the two main crops in this region, and (2) corn and soybean are two of three crops (the third one being cotton) that have greatly benefited from biotechnology during the last two decades.

For each of the six inputs included in our analysis, a price index in each year (and in each state in the state-level analysis) was obtained from USDA (2017b). Input quantity indices were obtained by dividing input cost by the associated price indices. For labor, energy, and fertilizer, the price and quantity indices were obtained from Eldon Ball at USDA (2017b). For herbicides and insecticides, the input prices were obtained from Richard Nehring at ERS, following the hedonic procedure proposed by Fernandez-Cornejo and Jans (1995). For “other inputs,” the price index and quantity index were calculated using a Fisher index applied to the remaining inputs (feed, seed, purchased services, and other intermediate inputs). Finally, the quantity of “intermediate output” *y* was measured using a Fisher quantity index (Diewert, 1992).^{4} Summary statistics for the U.S. data are reported in Table 1.

Table 1. Summary Statistics for U.S. Agriculture

The adoption rates *Bt*(*t*) and *HT*(*t*), at both the U.S. level (for the U.S. analysis) and the state-level (for the Corn Belt analysis), were obtained from Fernandez-Cornejo et al. (2014), USDA (2017a), and the Dmrkynetec farm survey.^{5} Note that biotechnology started being adopted in 1995, thus covering 19 years in our U.S. sample (from 1995 to 2013). To make the parameters of the variables *t*, *Bt*(*t*), and *HT*(*t*) comparable in equations (7a) and (7b), we define *Bt*(*t*) = [19* (observed proportional adoption rate of *Bt* technology)] and *HT*(*t*) = [19* (observed proportional adoption rate of *HT* technology)]. The parameters *d* and *e* in equations (7a) and (7b) provide a basis to evaluate the effects of biotechnology adoption on U.S. agriculture, with separate effects for Bt technology and HT technology. Bt can be viewed as an insecticide substitute. HT can be viewed as an herbicide complement for the corresponding herbicide product but a substitute for other herbicides (e.g., Fernandez-Cornejo et al., 2012). Note that our analysis is applied to agriculture as a whole. It captures productivity effects that are specific to each crop as well as effects that occur across agricultural activities. The latter effects include the effects of crop rotation and of crop-livestock interactions. Although most previous analyses of biotechnology have been crop specific (e.g., Bustos, Caprettini and Ponticelli, 2016; Carpenter, 2010; Klümper and Qaim, 2014; Perry, Moschini, and Hennessy, 2016), our analysis includes the productivity effects of input use and covers a broader scope of agriculture across all production activities. In this context, we examine the effects of HT and Bt technology on farm productivity and on input use, especially on the demand for herbicide and insecticides separately.

## 4. Econometric Estimates

In a preliminary analysis of the data, we investigated the nature of returns to scale. As noted previously, constant returns to scale (CRS) corresponds to δ = 1 in equation (7a). We tested the null hypothesis of CRS (H_{0}: δ = 1) using both U.S. aggregate data and state-level Corn Belt data. We estimated the model by the generalized method of moments using ln(*y* _{t − 1}) as instrument for ln(*y*_{t}). In this context, we failed to reject the null hypothesis at the 9% significance level with U.S. data and at the 70% significance level using state-level Corn Belt data. Thus, we did not find statistical evidence against CRS. On that basis, the analysis presented subsequently was conducted imposing CRS with δ = 1 in equation (7a). In addition, note that CRS offers a significant advantage for our empirical investigation: under CRS, there is no parameter associated with output *y* in equations (7a) and (7b). It means that the presence of measurement errors in *y* only affects the estimated variance of the error term in equation (7a), and it has no effect on the remaining parameter estimates. In other words, the estimation of all parameters in equations (7a) and (7b) are robust to the mismeasurement of intermediate output *y*.^{6} This feature is important in agriculture as production uncertainty makes the measurement of output somewhat problematic (e.g., Chavas, 2008; Pope and Chavas, 1994).

Assuming δ = 1, the translog model given in equations (7a) and (7b) constitutes a system of equations. Allowing for different variances and nonzero covariances across equations, the system was estimated by maximum likelihood (after imposing the homogeneity and symmetry restrictions discussed previously). To explore possible serial correlation, we allowed the error terms ε in equations (7a) and (7b) to exhibit first-order serial correlation, where ε_{it} = ρ_{i} ε_{i, t − 1}, and ρ_{i} is the serial correlation coefficient for the *i*th equation, *i* = 0, . . ., 5. The analysis was applied to the U.S.-level data over the period 1960–2013 and to the state-level data from the Corn Belt over the period 1960–2004. For the state-level analysis, the estimation was pooled across states, with state dummies being added to each equation to capture possible heterogeneity across Corn Belt states. The state dummies were introduced to be as intercept shifters in the cost equation (7a) and the cost share equation (7b), reflecting possible differences in technology across states, and they were introduced as interaction effects with the time trend variable *t* in the cost equation (7a), capturing possible differences in productivity growth across states.^{7}

The econometric results are reported in Table 2, where the subscript stands for the corresponding input: “1” for labor, “2” for energy, “3” for fertilizer, “4” for herbicides, “5” for insecticides, and “6” for other inputs.

Table 2. Parameter Estimates of the Translog Cost Function in Equations (7a) and (7b)

Table 2 shows that many estimated parameters are statistically significant. As reflected by the coefficients *a*, input prices have significant effects on input demands. Also, most of the time trend parameters *b* are statistically significant, indicating the presence of important technological change in U.S. agriculture during the last 50 years. In addition, several of the *d* and *e* parameters are statistically significant, indicating that biotechnology is among the important factors affecting technological change. The exact nature of these effects is further examined subsequently. Finally, in our state-level analysis, many of the state dummy variables (not reported in Table 2) were also found to be statistically significant (see Table 3).^{8}

Table 3. Hypothesis Testing

As discussed in Section 2, the cost function *C*(*r*, *y*, *t*) is concave in prices *r*. We investigated whether the estimates reported in Table 2 satisfy this property. The concavity of *C*(*r*, .) means that the matrix ${{{\partial ^2}C}/ {\partial {{{\bf r}}^2}}}$ is negative semidefinite, all its eigenvalues being nonpositive. We evaluated the eigenvalues of ${{{\partial ^2}C}/ {\partial {{{\bf r}}^2}}}$ at all data points in our U.S. sample. We found that all eigenvalues were not always less than or equal to zero. Based on the estimated distribution of the parameters reported in Table 2, we used Monte Carlo simulation to simulate the distribution of the eigenvalues at each data point. Using these simulated distributions, we tested the hypothesis that all eigenvalues are nonpositive. We found that, when positive, the eigenvalues were not statistically different from zero at the 10% significance level. On that basis, we conclude that, in our U.S. sample, there is no strong statistical evidence against the concavity of the estimated cost function.

To support our analysis of the effects of technological change, we conducted several formal tests. The test results are reported in Table 3. First, we tested the hypothesis of no technological change. It corresponds to the null hypothesis that all parameters *b*, *d*, and *e* are jointly zero. Using a Wald test, Table 3 provides strong evidence against this null hypothesis both at the national level and at the state level (with *P* values less than 0.01), which confirms a large impact of technological change on U.S. agriculture. Next, we investigated the nature of technological change. We tested whether technological change was “Hicks neutral” (i.e., whether it would not affect the input cost shares). From equation (6b), Hicks neutral technological change corresponds to the parameters (*b*_{i}, *d*_{i}, *e*_{i}) for factor *i* being all zero for all *i* = 1, . . ., 6. Using a Wald test, Table 3 shows that Hicks neutral technological change is strongly rejected for all factors both at the national level and the state level (with *P* values less than 0.01). Thus, consistent with previous research (e.g., Binswanger, 1974), we find strong evidence that technological change is “Hicks biased” and has significant effects on input cost shares. The exact nature of this bias is further discussed subsequently. Finally, in the state-level analysis, we examined possible heterogeneity in productivity across states. This involved testing the null hypothesis that all coefficients associated with the state dummy variables (as cost shifters, as cost share shifters, and as interactions with time trend) are zero. As reported in Table 3, we strongly reject this null hypothesis (with a *P* value less than 0.01), indicating the presence of much heterogeneity in agricultural productivity across states in the Corn Belt. This is consistent with the results obtained by Lusk, Tack, and Hendricks (2017). We also investigated whether productivity growth was similar across states. This was done by testing the null hypothesis that the coefficients of interaction variables between the state dummies and time trend are zero. As reported in Table 3, we rejected this null hypothesis at the 0.023 significance level, providing evidence of heterogeneity in productivity growth across states in the Corn Belt. The differences in productivity growth across states are reported in Table 4 and discussed subsequently.

Table 4. Rate of Technological Change (annual percentage)

## 5. Economic Implications

The estimates of equations (7a) and (7b) reported in Table 2 provide all the information necessary to evaluate agricultural technology and farm input demands. First, the rate of technological change (*RTC*) can be obtained from equation (6a). The estimated *RTC* (measured in annual percentage) is reported in Table 4 for selected periods. Table 4 shows that U.S. agriculture has exhibited rapid technological progress over the last few decades. The *RTC* goes from 1.29% to 2.60%. These results can be compared with previous USDA estimates of *RTC* obtained by Ball et al. (1997), Ball, Hallahan, and Nehring (2004), and Wang et al. (2015). All estimates reflect rapid productivity growth in agriculture. Our pre-1995 *RTC* estimate is 2.57; it is broadly consistent with the estimate of 2.65 reported by Ball et al. (1997) for the period 1960–1994.^{9}
Table 4 reports that, at the U.S. level, *RTC* declines from 2.57 before 1995 to 1.65 after 1995. This pattern indicates some slowdown of technological progress in U.S. agriculture. Again, this result is consistent with previous evidence (e.g., Wang et al., 2015).

However, our results differ in the Corn Belt. Table 4 reports *RTC* for each of the nine Corn Belt states as well as the average *RTC* for the Corn Belt. It shows that Illinois exhibits a high *RTC* varying from 3.19 in the 1960s to 3.85 in the 2000s. In contrast, Minnesota has an *RTC* going from 1.23 in the 1960s to 1.94 in the 2000s. This documents significant heterogeneity in productivity growth among Corn Belt states. The average *RTC* was 2.53 in the Corn Belt before 1995, but that number has increased to 2.96 after 1995. Thus, on average, the Corn Belt had a slightly lower productivity growth than the United States before 1995, but its productivity growth has increased since 1995 and is now ahead of the rest of United States. Since the year 1995 marks the start of the biotechnology revolution (i.e., the inception of GM commercial crops in U.S. agriculture), our analysis shows that the Corn Belt has benefited from biotechnology, and it has benefited more than the rest of the United States. This observation is not surprising: adoption of biotechnology has been rapid for corn and soybean (Fernandez-Cornejo et al., 2014), and corn and soybean are the two major crops grown in the Corn Belt. This result indicates that biotechnology has been a major driving factor of agricultural productivity in the United States. It also indicates that other U.S. regions (besides the Corn Belt) have not benefited as much from biotechnology, thus resulting in some slowdown in agricultural productivity growth. This slowdown is of some concern. Declining productivity growth may make it more difficult to feed a growing world population. A scenario where population grows faster than farm productivity would be associated with increased food insecurity and rising food prices. Such arguments stress the importance of research and development (both private and public) as key drivers of future agricultural productivity.

Second, our analysis allowed us to estimate the bias in technological change. The bias is given by the term *B*_{i} = ∂*w*_{i}/∂*t* in equation (6b), where technological change is said to be the *ith* factor-using if *B*_{i} > 0 and the *ith* factor-saving if *B*_{i} < 0. Before 1995 and from equation (7b), we have *B*_{i} = *b*_{i}. The coefficients *d*_{i} and *e*_{i} capture the changes in bias since 1995 because of the adoption of Bt and HT technology, respectively. As reported in Table 3, we found strong statistical evidence of bias in technological change. Recall that we consider six inputs: (1) labor, (2) energy, (3) fertilizer, (4) herbicides, (5) insecticides, and (6) other inputs. For both the U.S. and the Corn Belt results, Table 2 shows strong evidence that technological change has been labor saving (as *b* _{1} is negative and statistically significant) and fertilizer using, herbicide using, and insecticide using (as the corresponding *b*_{i} values are positive and significant). In addition, Table 2 shows evidence of bias in favor of energy for Corn Belt states. These results are largely consistent with previous research (e.g., Binswanger, 1974).

Table 2 also reports the biases related to biotechnology, including evaluations of Bt technology (as captured by the parameters *d*) and HT technology (as captured by the parameters *e*). Such parameters measure the change in biases beyond the ones captured by the parameters *b*. From Table 2, the parameters *d* _{1} and *e* _{1} are not statistically different from zero, indicating that neither Bt nor HT technology has affected the labor-saving bias of technological change in U.S. agriculture. This result differs from Bustos, Caprettini, and Ponticelli (2016) who argued that HT technology contributed to labor-saving bias in Brazilian agriculture.

In addition, Table 2 reports that *b* _{5} and *e* _{5} are not statistically significant, indicating that neither Bt nor HT has affected the strong bias in favor of insecticide use that prevailed before 1995. Although previous literature has argued that biotechnology has contributed to a reduction in pesticide use (e.g., Klümper and Qaim, 2014), our analysis indicates that this result applies to herbicide (as discussed subsequently), but not to insecticide: neither Bt nor HT have reduced the bias toward insecticide use in U.S. agriculture. This likely reflects the fact that the insects targeted by Bt technology (e.g., the European corn borer and rootworms for corn) are not easily controlled using traditional insecticides.

For both the United States and the Corn Belt states, the parameter *d* _{3} is found to be positive and statistically significant at the 10% level, indicating that Bt technology has increased the bias in favor of fertilizer use. This finding is important: by improving pest control, Bt technology helps reduce pest damages, making it easier for the plant to benefit from fertilizer applications.

For both the United States and the Corn Belt states, the parameters *e* _{3} and *e* _{4} are negative and statistically significant at the 10% level, providing evidence that HT technology has reduced the input-using bias for fertilizer and herbicide. Having *b* _{3} > 0, *e* _{3} < 0, and *b* _{3} + *e* _{3} > 0 indicates that this bias in favor of using fertilizer was reduced but not eliminated by HT. For herbicide use at the U.S. level, we have *b* _{4} > 0, *e* _{4} < 0, and *b* _{4} + *e* _{4} < 0, implying that HT was associated with a switch in technological change bias from herbicide using before 1995 to herbicide saving after 1995. This is another important finding: HT technology behaves as a substitute for herbicide use. Note that this finding is consistent with the results obtained by Fernandez-Cornejo et al. (2012) and Klümper and Qaim (2014).^{10} To the extent that reducing herbicide use is seen as being desirable from an environmental viewpoint, it indicates that, beyond improving weed control and reducing yield loss from weed infestation, biotechnology can generate environmental benefits. Yet, the patterns differ for the Corn Belt states, where we find that *b* _{4} > 0, *e* _{4} < 0, and *b* _{4} + *e* _{4} > 0. Thus, in the Corn Belt states, HT technology reduces the bias in favor of using herbicide but does not eliminate it, indicating weaker substitution between HT and pesticide use. This reflects apparent regional heterogeneity in the effects of biotechnology on agriculture.

Another difference between the United States and Corn Belt results involves energy use. For the United States, the estimates of *b* _{2}, *d* _{2}, or *e* _{2} are not statistically significant, indicating no bias in technical change with respect to energy use. However, the estimates differ for the Corn Belt where *b* _{2} and *e* _{2} are statistically significant at the 5% level, with *b* _{2} > 0, *e* _{2} < 0, and *b* _{2} + *e* _{2} < 0 implying a switch in biased technical change from energy using before 1995 to energy saving after 1995. This result likely reflects the fact that HT technology has been associated with reduced tillage (Fernandez-Cornejo et al., 2012; Perry, Moschini, and Hennessy, 2016).

Next, we evaluate the price elasticities of input demand. These estimates are obtained from equation (4) and reported in Tables 5 and 6. For the United States, Table 5 shows the own-price and cross-price elasticities for input demand evaluated at sample means. The own-price elasticities vary from −0.149 for “other inputs” to −1.008 for insecticides. With the exception of insecticides, all input demands are price inelastic. The results show that labor, energy, and other inputs have highly inelastic demands (with elasticities between −0.15 and −0.25). Demand for fertilizer and herbicides are also inelastic but are relatively more price sensitive (all around −0.75). The cross-price elasticities tend to be positive, indicating that most inputs are substitutes.^{11} The cross-price elasticities are 0.345 for herbicide demand with respect to insecticide price and 0.371 for insecticide demand with respect to energy price, both being statistically significant.

Table 5. Price Elasticities of Input Demand: U.S. Level, Evaluated at Sample Means

Table 6. Evolution of Own Price Elasticities for Selected Inputs: U.S. Level

Finally, Table 6 reports the evolution of own-price elasticities over time for the United States. Table 6 shows that the own-price elasticity for other inputs is fairly constant over time. It also reveals that the demands for fertilizer, herbicide, and insecticide are becoming much more price-inelastic over time. For example, the demand elasticity for fertilizer changed from −0.95 in the 1970s to −0.74 in the 1990s and to −0.17 in the 2000s. This increased inelasticity of demand implies that farmers are becoming less responsive to prices for fertilizer, herbicide, and insecticide. Note that biotechnology has contributed to reducing the adverse effects of pest and weed damages. If pest and weed damages reduce the farmers’ incentive to use fertilizers, then the adoption of biotechnology would be associated with stronger incentives to use fertilizers. Our results indicate that such changing incentives are associated with less demand sensitivity to input prices for fertilizer, herbicide, and insecticide. In other words, although U.S. farmers have benefited from rapid technological progress, their input choices have now become less sensitive to changing market conditions.

## 6. Conclusion

This article has explored the effects of biotechnology on farm productivity and input demands, with an application to U.S. agriculture. The analysis relies on a cost specification involving six inputs (labor, energy, fertilizer, herbicide, insecticide, and other inputs) and evaluating output as “intermediate output.” We argue that focusing on intermediate output helps validate cost minimization in the presence of production uncertainty. Also, the distinction between herbicide and insecticide is relevant as it allows us to evaluate the separate effects of two aspects of GM technology: Bt technology (targeted to improving pest control) and HT technology (targeted to improving weed control).

Our empirical analysis is applied to two agricultural data sets: U.S. data covering the period 1960–2013 and data for nine Corn Belt states covering the period 1960–2004. Cost and cost share equations are specified and estimated, providing useful information on the speed and nature of technological change, with a special focus on GM technology. The results document the changing patterns of farm productivity under biotechnology. They find that biotechnology has contributed to speeding up productivity growth in the Corn Belt, but not at the U.S. level. The results also document the evolving biases in technological change in agriculture, with a special focus on the demand for herbicides and insecticides. We find evidence that Bt technology has increased the bias in favor of fertilizer use. By reducing pest damages, this indicates that Bt technology makes it easier for the plant to benefit from fertilizer applications. We also find that HT technology has reduced the technical change bias in favor of herbicide use. Finally, we find evidence that farm demands for fertilizer, herbicide, and insecticide have become more inelastic, (i.e., less responsive to prices). Thus, although biotechnology has contributed to technological progress in agriculture, GM adoption has also been associated with a lower ability of farmers to adjust to changing market conditions.

Our results tend to support a growing literature regarding the impact of biotechnology in agriculture. For example, in the Corn Belt states, we find that the bias in technical change has changed from energy using before 1995 to energy saving after 1995. This result is consistent with HT technology being a complement to reduced tillage (Fernandez-Cornejo et al., 2012; Perry, Moschini, and Hennessy, 2016). We also document the heterogeneity in productivity both over time and across space. We find that, since 1995, agricultural productivity has increased faster in the Corn Belt than at the U.S. level, likely reflecting regional differences in biotechnology adoption. Finally, we documented evolving patterns of elasticities of farm input demands in the United States, with some trends toward more inelastic demands. Such trends raise several issues that appear to be policy relevant. The last few decades have seen a rise in concentration in farm input industries (Fuglie et al., 2012). Biotechnology firms have been vertically integrating into seed breeding and chemical production. In the presence of inelastic demand for inputs, increased concentration in farm input industries may contribute to the exercise of market power, leading to higher farm input prices. This change could have adverse effects on farm welfare and on the efficiency of agriculture. Exploring the economic and policy implications related to such issues appear to be good topics for future research.

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